Member State report / Art11 / 2020 / D6 / Croatia / Mediterranean: Adriatic Sea

Report type Member State report to Commission
MSFD Article Art. 11 Monitoring programmes (and Art. 17 updates)
Report due 2020-10-15
GES Descriptor D6 Sea-floor integrity/D1 Benthic habitats
Member State Croatia
Region/subregion Mediterranean: Adriatic Sea
Reported by Institute of Oceanography and Fisheries
Report date 2020-10-15
Report access

Descriptor
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
D6/D1
Monitoring strategy description
To date, the Republic of Croatia has not developed methods to monitor the state of the seabed under Descriptor 6 (MSFD). The European Commission (DG Environment) has established a technical group for seabed habitats and seabed integrity (TG Seabed) which aims to find a common methodology and way to assess the state of the seabed. No concrete methods and limits have yet been proposed to be used to assess the state of the seabed under this descriptor, and the technical group will continue to operate during 2020. Until a common methodology is found at the level of the European Community, the state of the seabed in the territorial waters of the Republic of Croatia will be determined on the basis of the state of associated habitats, ie benthic communities. Monitoring of the state of the seabed in areas affected by fishing activities, in the channels between the islands and in the open sea, will be performed on the basis of research on the state of invertebrate communities inhabiting these areas, related to criteria D6C3, D6C4 and D6C5. Monitoring of the state of the seabed at shallow depths in the coastal area will be performed on the basis of research on the condition of Posidonia oceanica meadows , related to criteria D6C3, D6C4 and D6C5. Monitoring of the seabed condition in the shallowest area of ​​the rocky coast will be performed by examining the condition of macroalgal communities in the mediolittoral and in the upper infralittoral, related to criteria D6C3, D6C4 and D6C5.
To date, the Republic of Croatia has not developed methods to monitor the state of the seabed under Descriptor 6 (MSFD). The European Commission (DG Environment) has established a technical group for seabed habitats and seabed integrity (TG Seabed) which aims to find a common methodology and way to assess the state of the seabed. No concrete methods and limits have yet been proposed to be used to assess the state of the seabed under this descriptor, and the technical group will continue to operate during 2020. Until a common methodology is found at the level of the European Community, the state of the seabed in the territorial waters of the Republic of Croatia will be determined on the basis of the state of associated habitats, ie benthic communities. Monitoring of the state of the seabed in areas affected by fishing activities, in the channels between the islands and in the open sea, will be performed on the basis of research on the state of invertebrate communities inhabiting these areas, related to criteria D6C3, D6C4 and D6C5. Monitoring of the state of the seabed at shallow depths in the coastal area will be performed on the basis of research on the condition of Posidonia oceanica meadows , related to criteria D6C3, D6C4 and D6C5. Monitoring of the seabed condition in the shallowest area of ​​the rocky coast will be performed by examining the condition of macroalgal communities in the mediolittoral and in the upper infralittoral, related to criteria D6C3, D6C4 and D6C5.
To date, the Republic of Croatia has not developed methods to monitor the state of the seabed under Descriptor 6 (MSFD). The European Commission (DG Environment) has established a technical group for seabed habitats and seabed integrity (TG Seabed) which aims to find a common methodology and way to assess the state of the seabed. No concrete methods and limits have yet been proposed to be used to assess the state of the seabed under this descriptor, and the technical group will continue to operate during 2020. Until a common methodology is found at the level of the European Community, the state of the seabed in the territorial waters of the Republic of Croatia will be determined on the basis of the state of associated habitats, ie benthic communities. Monitoring of the state of the seabed in areas affected by fishing activities, in the channels between the islands and in the open sea, will be performed on the basis of research on the state of invertebrate communities inhabiting these areas, related to criteria D6C3, D6C4 and D6C5. Monitoring of the state of the seabed at shallow depths in the coastal area will be performed on the basis of research on the condition of Posidonia oceanica meadows , related to criteria D6C3, D6C4 and D6C5. Monitoring of the seabed condition in the shallowest area of ​​the rocky coast will be performed by examining the condition of macroalgal communities in the mediolittoral and in the upper infralittoral, related to criteria D6C3, D6C4 and D6C5.
To date, the Republic of Croatia has not developed methods to monitor the state of the seabed under Descriptor 6 (MSFD). The European Commission (DG Environment) has established a technical group for seabed habitats and seabed integrity (TG Seabed) which aims to find a common methodology and way to assess the state of the seabed. No concrete methods and limits have yet been proposed to be used to assess the state of the seabed under this descriptor, and the technical group will continue to operate during 2020. Until a common methodology is found at the level of the European Community, the state of the seabed in the territorial waters of the Republic of Croatia will be determined on the basis of the state of associated habitats, ie benthic communities. Monitoring of the state of the seabed in areas affected by fishing activities, in the channels between the islands and in the open sea, will be performed on the basis of research on the state of invertebrate communities inhabiting these areas, related to criteria D6C3, D6C4 and D6C5. Monitoring of the state of the seabed at shallow depths in the coastal area will be performed on the basis of research on the condition of Posidonia oceanica meadows , related to criteria D6C3, D6C4 and D6C5. Monitoring of the seabed condition in the shallowest area of ​​the rocky coast will be performed by examining the condition of macroalgal communities in the mediolittoral and in the upper infralittoral, related to criteria D6C3, D6C4 and D6C5.
To date, the Republic of Croatia has not developed methods to monitor the state of the seabed under Descriptor 6 (MSFD). The European Commission (DG Environment) has established a technical group for seabed habitats and seabed integrity (TG Seabed) which aims to find a common methodology and way to assess the state of the seabed. No concrete methods and limits have yet been proposed to be used to assess the state of the seabed under this descriptor, and the technical group will continue to operate during 2020. Until a common methodology is found at the level of the European Community, the state of the seabed in the territorial waters of the Republic of Croatia will be determined on the basis of the state of associated habitats, ie benthic communities. Monitoring of the state of the seabed in areas affected by fishing activities, in the channels between the islands and in the open sea, will be performed on the basis of research on the state of invertebrate communities inhabiting these areas, related to criteria D6C3, D6C4 and D6C5. Monitoring of the state of the seabed at shallow depths in the coastal area will be performed on the basis of research on the condition of Posidonia oceanica meadows , related to criteria D6C3, D6C4 and D6C5. Monitoring of the seabed condition in the shallowest area of ​​the rocky coast will be performed by examining the condition of macroalgal communities in the mediolittoral and in the upper infralittoral, related to criteria D6C3, D6C4 and D6C5.
To date, the Republic of Croatia has not developed methods to monitor the state of the seabed under Descriptor 6 (MSFD). The European Commission (DG Environment) has established a technical group for seabed habitats and seabed integrity (TG Seabed) which aims to find a common methodology and way to assess the state of the seabed. No concrete methods and limits have yet been proposed to be used to assess the state of the seabed under this descriptor, and the technical group will continue to operate during 2020. Until a common methodology is found at the level of the European Community, the state of the seabed in the territorial waters of the Republic of Croatia will be determined on the basis of the state of associated habitats, ie benthic communities. Monitoring of the state of the seabed in areas affected by fishing activities, in the channels between the islands and in the open sea, will be performed on the basis of research on the state of invertebrate communities inhabiting these areas, related to criteria D6C3, D6C4 and D6C5. Monitoring of the state of the seabed at shallow depths in the coastal area will be performed on the basis of research on the condition of Posidonia oceanica meadows , related to criteria D6C3, D6C4 and D6C5. Monitoring of the seabed condition in the shallowest area of ​​the rocky coast will be performed by examining the condition of macroalgal communities in the mediolittoral and in the upper infralittoral, related to criteria D6C3, D6C4 and D6C5.
To date, the Republic of Croatia has not developed methods to monitor the state of the seabed under Descriptor 6 (MSFD). The European Commission (DG Environment) has established a technical group for seabed habitats and seabed integrity (TG Seabed) which aims to find a common methodology and way to assess the state of the seabed. No concrete methods and limits have yet been proposed to be used to assess the state of the seabed under this descriptor, and the technical group will continue to operate during 2020. Until a common methodology is found at the level of the European Community, the state of the seabed in the territorial waters of the Republic of Croatia will be determined on the basis of the state of associated habitats, ie benthic communities. Monitoring of the state of the seabed in areas affected by fishing activities, in the channels between the islands and in the open sea, will be performed on the basis of research on the state of invertebrate communities inhabiting these areas, related to criteria D6C3, D6C4 and D6C5. Monitoring of the state of the seabed at shallow depths in the coastal area will be performed on the basis of research on the condition of Posidonia oceanica meadows , related to criteria D6C3, D6C4 and D6C5. Monitoring of the seabed condition in the shallowest area of ​​the rocky coast will be performed by examining the condition of macroalgal communities in the mediolittoral and in the upper infralittoral, related to criteria D6C3, D6C4 and D6C5.
To date, the Republic of Croatia has not developed methods to monitor the state of the seabed under Descriptor 6 (MSFD). The European Commission (DG Environment) has established a technical group for seabed habitats and seabed integrity (TG Seabed) which aims to find a common methodology and way to assess the state of the seabed. No concrete methods and limits have yet been proposed to be used to assess the state of the seabed under this descriptor, and the technical group will continue to operate during 2020. Until a common methodology is found at the level of the European Community, the state of the seabed in the territorial waters of the Republic of Croatia will be determined on the basis of the state of associated habitats, ie benthic communities. Monitoring of the state of the seabed in areas affected by fishing activities, in the channels between the islands and in the open sea, will be performed on the basis of research on the state of invertebrate communities inhabiting these areas, related to criteria D6C3, D6C4 and D6C5. Monitoring of the state of the seabed at shallow depths in the coastal area will be performed on the basis of research on the condition of Posidonia oceanica meadows , related to criteria D6C3, D6C4 and D6C5. Monitoring of the seabed condition in the shallowest area of ​​the rocky coast will be performed by examining the condition of macroalgal communities in the mediolittoral and in the upper infralittoral, related to criteria D6C3, D6C4 and D6C5.
To date, the Republic of Croatia has not developed methods to monitor the state of the seabed under Descriptor 6 (MSFD). The European Commission (DG Environment) has established a technical group for seabed habitats and seabed integrity (TG Seabed) which aims to find a common methodology and way to assess the state of the seabed. No concrete methods and limits have yet been proposed to be used to assess the state of the seabed under this descriptor, and the technical group will continue to operate during 2020. Until a common methodology is found at the level of the European Community, the state of the seabed in the territorial waters of the Republic of Croatia will be determined on the basis of the state of associated habitats, ie benthic communities. Monitoring of the state of the seabed in areas affected by fishing activities, in the channels between the islands and in the open sea, will be performed on the basis of research on the state of invertebrate communities inhabiting these areas, related to criteria D6C3, D6C4 and D6C5. Monitoring of the state of the seabed at shallow depths in the coastal area will be performed on the basis of research on the condition of Posidonia oceanica meadows , related to criteria D6C3, D6C4 and D6C5. Monitoring of the seabed condition in the shallowest area of ​​the rocky coast will be performed by examining the condition of macroalgal communities in the mediolittoral and in the upper infralittoral, related to criteria D6C3, D6C4 and D6C5.
Coverage of GES criteria
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Gaps and plans
The methods to monitor the state of the seabed under Descriptor 6 (MSFD) has not been developed. No concrete methods and threshold values have yet been proposed to be used to assess the state of the seabed under this descriptor.
The methods to monitor the state of the seabed under Descriptor 6 (MSFD) has not been developed. No concrete methods and threshold values have yet been proposed to be used to assess the state of the seabed under this descriptor.
The methods to monitor the state of the seabed under Descriptor 6 (MSFD) has not been developed. No concrete methods and threshold values have yet been proposed to be used to assess the state of the seabed under this descriptor.
The methods to monitor the state of the seabed under Descriptor 6 (MSFD) has not been developed. No concrete methods and threshold values have yet been proposed to be used to assess the state of the seabed under this descriptor.
The methods to monitor the state of the seabed under Descriptor 6 (MSFD) has not been developed. No concrete methods and threshold values have yet been proposed to be used to assess the state of the seabed under this descriptor.
The methods to monitor the state of the seabed under Descriptor 6 (MSFD) has not been developed. No concrete methods and threshold values have yet been proposed to be used to assess the state of the seabed under this descriptor.
The methods to monitor the state of the seabed under Descriptor 6 (MSFD) has not been developed. No concrete methods and threshold values have yet been proposed to be used to assess the state of the seabed under this descriptor.
The methods to monitor the state of the seabed under Descriptor 6 (MSFD) has not been developed. No concrete methods and threshold values have yet been proposed to be used to assess the state of the seabed under this descriptor.
The methods to monitor the state of the seabed under Descriptor 6 (MSFD) has not been developed. No concrete methods and threshold values have yet been proposed to be used to assess the state of the seabed under this descriptor.
Related targets
  • D6T1
  • D6T2
  • D6T3
  • D6T4
  • D6T5
  • D6T6
  • D6T1
  • D6T2
  • D6T3
  • D6T4
  • D6T5
  • D6T6
  • D6T1
  • D6T2
  • D6T3
  • D6T4
  • D6T5
  • D6T6
  • D6T1
  • D6T2
  • D6T3
  • D6T4
  • D6T5
  • D6T6
  • D6T1
  • D6T2
  • D6T3
  • D6T4
  • D6T5
  • D6T6
  • D6T1
  • D6T2
  • D6T3
  • D6T4
  • D6T5
  • D6T6
  • D6T1
  • D6T2
  • D6T3
  • D6T4
  • D6T5
  • D6T6
  • D6T1
  • D6T2
  • D6T3
  • D6T4
  • D6T5
  • D6T6
  • D6T1
  • D6T2
  • D6T3
  • D6T4
  • D6T5
  • D6T6
Coverage of targets
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Related measures
Coverage of measures
Related monitoring programmes
  • MADHR-D06-01
  • MADHR-D06-02
  • MADHR-D06-03
  • MADHR-D06-01
  • MADHR-D06-02
  • MADHR-D06-03
  • MADHR-D06-01
  • MADHR-D06-02
  • MADHR-D06-03
  • MADHR-D06-01
  • MADHR-D06-02
  • MADHR-D06-03
  • MADHR-D06-01
  • MADHR-D06-02
  • MADHR-D06-03
  • MADHR-D06-01
  • MADHR-D06-02
  • MADHR-D06-03
  • MADHR-D06-01
  • MADHR-D06-02
  • MADHR-D06-03
  • MADHR-D06-01
  • MADHR-D06-02
  • MADHR-D06-03
  • MADHR-D06-01
  • MADHR-D06-02
  • MADHR-D06-03
Programme code
MADHR-D06-01
MADHR-D06-01
MADHR-D06-01
MADHR-D06-02
MADHR-D06-02
MADHR-D06-02
MADHR-D06-03
MADHR-D06-03
MADHR-D06-03
Programme name
Seabed habitats - community characteristics
Seabed habitats - community characteristics
Seabed habitats - community characteristics
Seabed habitats - community characteristics
Seabed habitats - community characteristics
Seabed habitats - community characteristics
Seabed habitats - community characteristics
Seabed habitats - community characteristics
Seabed habitats - community characteristics
Update type
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Old programme codes
  • MADHR-D0146-01
  • MADHR-D0146-03
  • MADHR-D0146-01
  • MADHR-D0146-03
  • MADHR-D0146-01
  • MADHR-D0146-03
  • MADHR-D0146-02
  • MADHR-D0146-02
  • MADHR-D0146-02
  • MADHR-D0146-04
  • MADHR-D0146-04
  • MADHR-D0146-04
Programme description
Until a common methodology for D6 is found at the level of the European Community, the state of the seabed in the territorial waters of the Republic of Croatia will be determined on the basis of the state of associated habitats, ie benthic communities. Monitoring of the state of the seabed in areas affected by fishing activities, in the channels between the islands and in the open sea, will be performed on the basis of research on the state of invertebrate communities inhabiting these areas, related to criteria D6C3, D6C4 and D6C5.Activities to monitor changes in the composition of benthic invertebrate communities include the collection of samples at 30 selected stations in the channels between the islands and in the open sea. The proposed stations are located on different types of substrates at depths up to 250 m. Monitoring will be performed once a year, in the summer period (June / July). Monitoring of invertebrate communities in areas affected by fishing Activities will be carried out using a scientific bottom trawl net. Technical and design features of the bottom trawl: mesh size and mesh opening, and speed ship (3 NM) should be constant at all stations, with a haul duration of 30 minutes. Sampling is done during daylight.
Until a common methodology for D6 is found at the level of the European Community, the state of the seabed in the territorial waters of the Republic of Croatia will be determined on the basis of the state of associated habitats, ie benthic communities. Monitoring of the state of the seabed in areas affected by fishing activities, in the channels between the islands and in the open sea, will be performed on the basis of research on the state of invertebrate communities inhabiting these areas, related to criteria D6C3, D6C4 and D6C5.Activities to monitor changes in the composition of benthic invertebrate communities include the collection of samples at 30 selected stations in the channels between the islands and in the open sea. The proposed stations are located on different types of substrates at depths up to 250 m. Monitoring will be performed once a year, in the summer period (June / July). Monitoring of invertebrate communities in areas affected by fishing Activities will be carried out using a scientific bottom trawl net. Technical and design features of the bottom trawl: mesh size and mesh opening, and speed ship (3 NM) should be constant at all stations, with a haul duration of 30 minutes. Sampling is done during daylight.
Until a common methodology for D6 is found at the level of the European Community, the state of the seabed in the territorial waters of the Republic of Croatia will be determined on the basis of the state of associated habitats, ie benthic communities. Monitoring of the state of the seabed in areas affected by fishing activities, in the channels between the islands and in the open sea, will be performed on the basis of research on the state of invertebrate communities inhabiting these areas, related to criteria D6C3, D6C4 and D6C5.Activities to monitor changes in the composition of benthic invertebrate communities include the collection of samples at 30 selected stations in the channels between the islands and in the open sea. The proposed stations are located on different types of substrates at depths up to 250 m. Monitoring will be performed once a year, in the summer period (June / July). Monitoring of invertebrate communities in areas affected by fishing Activities will be carried out using a scientific bottom trawl net. Technical and design features of the bottom trawl: mesh size and mesh opening, and speed ship (3 NM) should be constant at all stations, with a haul duration of 30 minutes. Sampling is done during daylight.
Until a common methodology is found at the level of the European Community, the state of the seabed in the territorial waters of the Republic of Croatia will be determined on the basis of the state of associated habitats, ie benthic communities. Monitoring of the state of the seabed at shallow depths in the coastal area will be performed on the basis of research on the condition of Posidonia oceanica meadows , related to criteria D6C3, D6C4 and D6C5. Posidonia oceanica meadows are consider to be habitats with highest diversity in Mediterranean Sea with important role in production of oxygen and organic matter and prevention of coastal erosion. Posidonia meadows are developed almost along entire Croatian coast and that is the reason way program of monitoring Posidonia oceanica will include stations along that area. Monitoring activities of Posidonia oceanica meadows include surveys at 45 stations in the coastal area, which are also included in the monitoring under the Water Framework Directive (Directive 2000/60 / EC).
Until a common methodology is found at the level of the European Community, the state of the seabed in the territorial waters of the Republic of Croatia will be determined on the basis of the state of associated habitats, ie benthic communities. Monitoring of the state of the seabed at shallow depths in the coastal area will be performed on the basis of research on the condition of Posidonia oceanica meadows , related to criteria D6C3, D6C4 and D6C5. Posidonia oceanica meadows are consider to be habitats with highest diversity in Mediterranean Sea with important role in production of oxygen and organic matter and prevention of coastal erosion. Posidonia meadows are developed almost along entire Croatian coast and that is the reason way program of monitoring Posidonia oceanica will include stations along that area. Monitoring activities of Posidonia oceanica meadows include surveys at 45 stations in the coastal area, which are also included in the monitoring under the Water Framework Directive (Directive 2000/60 / EC).
Until a common methodology is found at the level of the European Community, the state of the seabed in the territorial waters of the Republic of Croatia will be determined on the basis of the state of associated habitats, ie benthic communities. Monitoring of the state of the seabed at shallow depths in the coastal area will be performed on the basis of research on the condition of Posidonia oceanica meadows , related to criteria D6C3, D6C4 and D6C5. Posidonia oceanica meadows are consider to be habitats with highest diversity in Mediterranean Sea with important role in production of oxygen and organic matter and prevention of coastal erosion. Posidonia meadows are developed almost along entire Croatian coast and that is the reason way program of monitoring Posidonia oceanica will include stations along that area. Monitoring activities of Posidonia oceanica meadows include surveys at 45 stations in the coastal area, which are also included in the monitoring under the Water Framework Directive (Directive 2000/60 / EC).
Until a common methodology is found at the level of the European Community, the state of the seabed in the territorial waters of the Republic of Croatia will be determined on the basis of the state of associated habitats, ie benthic communities. Monitoring of the seabed condition in the shallowest area of ​​the rocky coast will be performed by examining the condition of macroalgal communities in the mediolittoral and in the upper infralittoral, related to criteria D6C3, D6C4 and D6C5. Activities for monitoring the condition of macroalgal communities include mapping of communities in the mediolittoral and in the upper infralittoral along the entire Croatian coastline. Monitoring of the seabed in the shallowest area of the rocky coast will be performed by investigating the condition of macroalgal communities in the mediolittoral and upper infralittoral in three-year cycles, which means that in a certain area (section of the coastline) monitoring should be done once in a period of three years.
Until a common methodology is found at the level of the European Community, the state of the seabed in the territorial waters of the Republic of Croatia will be determined on the basis of the state of associated habitats, ie benthic communities. Monitoring of the seabed condition in the shallowest area of ​​the rocky coast will be performed by examining the condition of macroalgal communities in the mediolittoral and in the upper infralittoral, related to criteria D6C3, D6C4 and D6C5. Activities for monitoring the condition of macroalgal communities include mapping of communities in the mediolittoral and in the upper infralittoral along the entire Croatian coastline. Monitoring of the seabed in the shallowest area of the rocky coast will be performed by investigating the condition of macroalgal communities in the mediolittoral and upper infralittoral in three-year cycles, which means that in a certain area (section of the coastline) monitoring should be done once in a period of three years.
Until a common methodology is found at the level of the European Community, the state of the seabed in the territorial waters of the Republic of Croatia will be determined on the basis of the state of associated habitats, ie benthic communities. Monitoring of the seabed condition in the shallowest area of ​​the rocky coast will be performed by examining the condition of macroalgal communities in the mediolittoral and in the upper infralittoral, related to criteria D6C3, D6C4 and D6C5. Activities for monitoring the condition of macroalgal communities include mapping of communities in the mediolittoral and in the upper infralittoral along the entire Croatian coastline. Monitoring of the seabed in the shallowest area of the rocky coast will be performed by investigating the condition of macroalgal communities in the mediolittoral and upper infralittoral in three-year cycles, which means that in a certain area (section of the coastline) monitoring should be done once in a period of three years.
Monitoring purpose
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
Other policies and conventions
  • Water Framework Directive
  • Water Framework Directive
  • Water Framework Directive
  • Water Framework Directive
  • Water Framework Directive
  • Water Framework Directive
Regional cooperation - coordinating body
Regional cooperation - countries involved
Regional cooperation - implementation level
Monitoring details
Monitoring of the seabed condition at shallower depths in the coastal area will be performed based on research of the condition of Posidonia oceanica meadows in three-year cycles, which means that each station should be monitored once every three years.
Monitoring of the seabed condition at shallower depths in the coastal area will be performed based on research of the condition of Posidonia oceanica meadows in three-year cycles, which means that each station should be monitored once every three years.
Monitoring of the seabed condition at shallower depths in the coastal area will be performed based on research of the condition of Posidonia oceanica meadows in three-year cycles, which means that each station should be monitored once every three years.
Features
Benthic broad habitats
Benthic broad habitats
Benthic broad habitats
Other benthic habitats
Other benthic habitats
Other benthic habitats
Other benthic habitats
Other benthic habitats
Other benthic habitats
Elements
  • Circalittoral mixed sediment
  • Circalittoral mud
  • Circalittoral sand
  • Offshore circalittoral mixed sediment
  • Offshore circalittoral mud
  • Offshore circalittoral sand
  • Upper bathyal sediment
  • Circalittoral mixed sediment
  • Circalittoral mud
  • Circalittoral sand
  • Offshore circalittoral mixed sediment
  • Offshore circalittoral mud
  • Offshore circalittoral sand
  • Upper bathyal sediment
  • Circalittoral mixed sediment
  • Circalittoral mud
  • Circalittoral sand
  • Offshore circalittoral mixed sediment
  • Offshore circalittoral mud
  • Offshore circalittoral sand
  • Upper bathyal sediment
  • Posidonia beds (Posidonion oceanicae)
  • Posidonia beds (Posidonion oceanicae)
  • Posidonia beds (Posidonion oceanicae)
  • Reefs
  • Reefs
  • Reefs
GES criteria
D6C3
D6C4
D6C5
D6C3
D6C4
D6C5
D6C3
D6C4
D6C5
Parameters
  • Extent
  • Extent
  • Extent
  • Extent
  • Extent
  • Extent
  • Extent
  • Extent
  • Extent
Parameter Other
Spatial scope
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
Marine reporting units
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
  • MAD-HR-MRU_1
Temporal scope (start date - end date)
2021-2026
2021-2026
2021-2026
2021-2026
2021-2026
2021-2026
2021-2026
2021-2026
2021-2026
Monitoring frequency
Yearly
Yearly
Yearly
Other
Other
Other
Other
Other
Other
Monitoring type
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling coastal
  • In-situ sampling coastal
  • In-situ sampling coastal
  • In-situ sampling coastal
  • In-situ sampling coastal
Monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
Monitoring method other
Sampling procedure has been described in Marasovic I., Krstulovic, N., Leder, N., Loncar, G., Precali, R., Šolic, M., Loncar,.G., Beg- Paklar, G., Bojanic, N., Cvitkovic, I., Dadic, V., Despalatovic, M., Dulcic, J., Grbec, B., Kušpilic, G., Nincevic-Gladan, Ž., P. Tutman, Ujevic, I., Vrgoc, N., Vukadin, P., Žuljevic, A. Coastal cities water pollution control project, Part C1: Monitoring and Observation System for Ongoing Assessment of the Adriatic sea under the Adriatic sea Monitoring Programme, Phase II. Interim report (IR), December, 2013. https://jadran.izor.hr/jadranski_projekt_2/MJERNE-METODE-I-OPREMA.pdf
Sampling procedure has been described in Marasovic I., Krstulovic, N., Leder, N., Loncar, G., Precali, R., Šolic, M., Loncar,.G., Beg- Paklar, G., Bojanic, N., Cvitkovic, I., Dadic, V., Despalatovic, M., Dulcic, J., Grbec, B., Kušpilic, G., Nincevic-Gladan, Ž., P. Tutman, Ujevic, I., Vrgoc, N., Vukadin, P., Žuljevic, A. Coastal cities water pollution control project, Part C1: Monitoring and Observation System for Ongoing Assessment of the Adriatic sea under the Adriatic sea Monitoring Programme, Phase II. Interim report (IR), December, 2013. https://jadran.izor.hr/jadranski_projekt_2/MJERNE-METODE-I-OPREMA.pdf
Sampling procedure has been described in Marasovic I., Krstulovic, N., Leder, N., Loncar, G., Precali, R., Šolic, M., Loncar,.G., Beg- Paklar, G., Bojanic, N., Cvitkovic, I., Dadic, V., Despalatovic, M., Dulcic, J., Grbec, B., Kušpilic, G., Nincevic-Gladan, Ž., P. Tutman, Ujevic, I., Vrgoc, N., Vukadin, P., Žuljevic, A. Coastal cities water pollution control project, Part C1: Monitoring and Observation System for Ongoing Assessment of the Adriatic sea under the Adriatic sea Monitoring Programme, Phase II. Interim report (IR), December, 2013. https://jadran.izor.hr/jadranski_projekt_2/MJERNE-METODE-I-OPREMA.pdf
Hrvatske vode (2015) Metodologija uzorkovanja, laboratorijskih analiza i određivanja omjera ekološke kakvoće bioloških elemenata kakvoće. 237 str. Link: https://www.voda.hr/sites/default/files/metodologija_uzorkovanja_laboratorijskih_analiza_i_odredivanja_omjera_ekoloske_kakvoce_bioloskih_elemenata_i_odluka.pdf
Hrvatske vode (2015) Metodologija uzorkovanja, laboratorijskih analiza i određivanja omjera ekološke kakvoće bioloških elemenata kakvoće. 237 str. Link: https://www.voda.hr/sites/default/files/metodologija_uzorkovanja_laboratorijskih_analiza_i_odredivanja_omjera_ekoloske_kakvoce_bioloskih_elemenata_i_odluka.pdf
Hrvatske vode (2015) Metodologija uzorkovanja, laboratorijskih analiza i određivanja omjera ekološke kakvoće bioloških elemenata kakvoće. 237 str. Link: https://www.voda.hr/sites/default/files/metodologija_uzorkovanja_laboratorijskih_analiza_i_odredivanja_omjera_ekoloske_kakvoce_bioloskih_elemenata_i_odluka.pdf
Hrvatske vode (2015) Metodologija uzorkovanja, laboratorijskih analiza i određivanja omjera ekološke kakvoće bioloških elemenata kakvoće. 237 str. Link: https://www.voda.hr/sites/default/files/metodologija_uzorkovanja_laboratorijskih_analiza_i_odredivanja_omjera_ekoloske_kakvoce_bioloskih_elemenata_i_odluka.pdf
Hrvatske vode (2015) Metodologija uzorkovanja, laboratorijskih analiza i određivanja omjera ekološke kakvoće bioloških elemenata kakvoće. 237 str. Link: https://www.voda.hr/sites/default/files/metodologija_uzorkovanja_laboratorijskih_analiza_i_odredivanja_omjera_ekoloske_kakvoce_bioloskih_elemenata_i_odluka.pdf
Hrvatske vode (2015) Metodologija uzorkovanja, laboratorijskih analiza i određivanja omjera ekološke kakvoće bioloških elemenata kakvoće. 237 str. Link: https://www.voda.hr/sites/default/files/metodologija_uzorkovanja_laboratorijskih_analiza_i_odredivanja_omjera_ekoloske_kakvoce_bioloskih_elemenata_i_odluka.pdf
Quality control
As used in reported monitoring method.
As used in reported monitoring method.
As used in reported monitoring method.
As used in the reported monitoring method.
As used in the reported monitoring method.
As used in the reported monitoring method.
As used in the reported monitoring method.
As used in the reported monitoring method.
As used in the reported monitoring method.
Data management
Data access
Related indicator/name
Contact
References