Member State report / Art11 / 2020 / D1-P / Estonia / Baltic 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 D1 Pelagic habitats
Member State Estonia
Region/subregion Baltic Sea
Reported by Estonian Environment Agency
Report date 2020-11-11
Report access

Descriptor
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Monitoring strategy description
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
The aim of the monitoring strategy "SD1.6 – Biological diversity – pelagic habitats” is to assess the status of pelagic habitats by collecting data on species composition, abundance and biomass of phytoplankton and zooplankton communities, as well as the physical and chemical conditions influencing their distribution and diversity. Following monitoring programmes produce data for the assessments of the status and impact, as well as pressures in the marine environment: "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Water column – physical characteristics", "Water column – chemical characteristics", "Nutrients in the water column", "Hydrological characteristics", "Ice", and "Non-indigenous species – harbours and adjacent regions". The main anthropogenic pressure to the pelagic habitats is the input of nutrients that is monitored in the frames of the programme “Inputs of nutrients and hazardous substances – land-based sources”. Information on the uses and human activities affecting the pelagic habitats is collected in the programme “Marine and coastal activities”.
Coverage of GES criteria
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Gaps and plans
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Monitoring frequency in the coastal water bodies (once per 6-year period, excluding monitoring areas with high monitoring frequency) does not provide sufficient data that could give a good overview of whether and to what extent human activities influence phytoplankton species composition, abundance, and biomass. The effect of anthropogenic pressures (eg nutrient levels) may be overridden by meteorological and hydrophysical conditions during the observations. Microzooplankton is not fully covered by monitoring. Zooplankton sampling methods need to be developed for shallow areas also (currently ZP monitoring methods require water depth at least 7 m). „Seasonal succession of dominating phytoplankton groups“ and „Zooplankton mean size and total stock“ indicators’ thresholds are not developed nor agreed for all sub-basins. For new methods as automated image analysis, HPLC pigment analysis, DNA sequencing, etc that could help to increase the frequency of monitoring, additional studies and pilot monitoring projects are needed as well as parallel measurement sessions during a long-time period. As only two status indicators have been currently used in an assessment, the need for additional indicators is under discussion (e.g. indicator „Zooplankton species diversity“ is being developed in cooperation with HELCOM).
Related targets
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
  • BALEE-T33
  • BALEE-T34
  • Target 16
  • Target 8
Coverage of targets
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Adequate monitoring was in place by 2018
Related measures
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
  • BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures'
  • BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread'
  • BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system'
  • BALEE-M009 - 'Creating ready-to-use liquefied natural gas (LNG) as ship fuel'
  • BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter'
Coverage of measures
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Related monitoring programmes
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
  • BALEE-D00-40_MarineAndCoastalActivities
  • BALEE-D010405-10_Phytop
  • BALEE-D010405-11_Zoopl
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-19_NISDynImpact
  • BALEE-D05-21_AlgalBlooms
  • BALEE-D05-23_NutrientWaterColumn
  • BALEE-D05-24_WaterColumnChem
  • BALEE-D0507-25_WaterColumnPhys
  • BALEE-D07-26_PhysCharWaves
  • BALEE-D07-27_Ice
Programme code
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D00-40_MarineAndCoastalActivities
BALEE-D010405-10_Phytop
BALEE-D010405-10_Phytop
BALEE-D010405-10_Phytop
BALEE-D010405-11_Zoopl
BALEE-D010405-11_Zoopl
BALEE-D010405-11_Zoopl
BALEE-D02-18_NISRiskAreas
BALEE-D02-18_NISRiskAreas
BALEE-D02-18_NISRiskAreas
BALEE-D02-18_NISRiskAreas
BALEE-D02-19_NISDynImpact
BALEE-D02-19_NISDynImpact
BALEE-D05-21_AlgalBlooms
BALEE-D05-21_AlgalBlooms
BALEE-D05-23_NutrientWaterColumn
BALEE-D05-23_NutrientWaterColumn
BALEE-D05-24_WaterColumnChem
BALEE-D05-24_WaterColumnChem
BALEE-D05-24_WaterColumnChem
BALEE-D0507-25_WaterColumnPhys
BALEE-D0507-25_WaterColumnPhys
BALEE-D0507-25_WaterColumnPhys
BALEE-D0507-25_WaterColumnPhys
BALEE-D0507-25_WaterColumnPhys
BALEE-D0507-25_WaterColumnPhys
BALEE-D0507-25_WaterColumnPhys
BALEE-D07-26_PhysCharWaves
BALEE-D07-26_PhysCharWaves
BALEE-D07-26_PhysCharWaves
BALEE-D07-26_PhysCharWaves
BALEE-D07-26_PhysCharWaves
BALEE-D07-26_PhysCharWaves
BALEE-D07-27_Ice
Programme name
Marine and coastal activities
Marine and coastal activities
Marine and coastal activities
Marine and coastal activities
Marine and coastal activities
Marine and coastal activities
Marine and coastal activities
Marine and coastal activities
Marine and coastal activities
Marine and coastal activities
Marine and coastal activities
Marine and coastal activities
Marine and coastal activities
Marine and coastal activities
Marine and coastal activities
Marine and coastal activities
Marine and coastal activities
Marine and coastal activities
Marine and coastal activities
Marine and coastal activities
Marine and coastal activities
Marine and coastal activities
Marine and coastal activities
Phytoplankton species composition, abundance and biomass
Phytoplankton species composition, abundance and biomass
Phytoplankton species composition, abundance and biomass
Zooplankton species composition, abundance and biomass
Zooplankton species composition, abundance and biomass
Zooplankton species composition, abundance and biomass
Non-indigenous species – harbours and adjacent regions
Non-indigenous species – harbours and adjacent regions
Non-indigenous species – harbours and adjacent regions
Non-indigenous species – harbours and adjacent regions
Non-indigenous species – abundance and biomass
Non-indigenous species – abundance and biomass
Harmful blooms (remote sensing)
Harmful blooms (remote sensing)
Nutrient levels in water column
Nutrient levels in water column
Water column – chemical characteristics
Water column – chemical characteristics
Water column – chemical characteristics
Water column – physical characteristics
Water column – physical characteristics
Water column – physical characteristics
Water column – physical characteristics
Water column – physical characteristics
Water column – physical characteristics
Water column – physical characteristics
Hydrological characteristics
Hydrological characteristics
Hydrological characteristics
Hydrological characteristics
Hydrological characteristics
Hydrological characteristics
Ice cover
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
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
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Old programme codes
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D00-39_CoastalOffshoreActivities
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-18_NISRiskAreas
  • BALEE-D02-18_NISRiskAreas
Programme description
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.
The aim of the programme is to monitor phytoplankton communities (species composition, abundance, biomass and seasonal cycle of dominant groups) in the water column. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD1.6 Biodiversity – pelagic habitats”, “SD4/SD1 Food webs / Biodiversity – ecosystems” and “SD2– Non-indigenous species”. The programme is related to GES Descriptor D5, Criterion D5C2, Descriptor D1, Criterion D1C6 and Descriptor D4, Criterion D4C1. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM divisions) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency of 5 to 12 times a year at the designated monitoring stations (at least 3 stations in each coastal water body and 11 in the Estonian off-shore areas). The program is regionally coordinated via HELCOM and the HELCOM monitoring manual is followed. Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). The threshold values for the indicator of seasonal succession of dominating phytoplankton groups are still missing for some assessment units of the Baltic Sea (incl. Estonian marine area), mainly due to the lack of data corresponding to the set criteria. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Pelagic habitats – community characteristics.
The aim of the programme is to monitor phytoplankton communities (species composition, abundance, biomass and seasonal cycle of dominant groups) in the water column. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD1.6 Biodiversity – pelagic habitats”, “SD4/SD1 Food webs / Biodiversity – ecosystems” and “SD2– Non-indigenous species”. The programme is related to GES Descriptor D5, Criterion D5C2, Descriptor D1, Criterion D1C6 and Descriptor D4, Criterion D4C1. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM divisions) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency of 5 to 12 times a year at the designated monitoring stations (at least 3 stations in each coastal water body and 11 in the Estonian off-shore areas). The program is regionally coordinated via HELCOM and the HELCOM monitoring manual is followed. Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). The threshold values for the indicator of seasonal succession of dominating phytoplankton groups are still missing for some assessment units of the Baltic Sea (incl. Estonian marine area), mainly due to the lack of data corresponding to the set criteria. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Pelagic habitats – community characteristics.
The aim of the programme is to monitor phytoplankton communities (species composition, abundance, biomass and seasonal cycle of dominant groups) in the water column. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD1.6 Biodiversity – pelagic habitats”, “SD4/SD1 Food webs / Biodiversity – ecosystems” and “SD2– Non-indigenous species”. The programme is related to GES Descriptor D5, Criterion D5C2, Descriptor D1, Criterion D1C6 and Descriptor D4, Criterion D4C1. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM divisions) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency of 5 to 12 times a year at the designated monitoring stations (at least 3 stations in each coastal water body and 11 in the Estonian off-shore areas). The program is regionally coordinated via HELCOM and the HELCOM monitoring manual is followed. Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). The threshold values for the indicator of seasonal succession of dominating phytoplankton groups are still missing for some assessment units of the Baltic Sea (incl. Estonian marine area), mainly due to the lack of data corresponding to the set criteria. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Pelagic habitats – community characteristics.
The aim of the programme is to monitor species composition, abundance and biomass of mesozooplankton. It provides data to monitoring strategy “SD1.6 Biodiversity – pelagic habitats”, as well as “SD2-Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptors D1, Criterion D1C6, Description D2 Criterions D2C1 and D2C2 and Descriptor D4 Criterion D4C2. Data are gathered to assess the state of the marine environment and environmental status in three coastal water bodies and all off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions) as well as pressures from/by non-indigenous species. Monitoring is conducted yearly with a frequency 10 times a year at the designated coastal monitoring stations (3 stations in each coastal water body) and with frequency twice a year for 16 stations in the Estonian off-shore areas. The program is regionally coordinated via HELCOM and the HELCOM guidelines are followed. Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). Mesozooplankton Mean Size Total Stock indicator is developed by HELCOM on the basis of mesozooplankton data. The threshold values for the indicator have been internationally agreed for some sub-basins, but not for the Gulf of Riga yet. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Pelagic habitats – community characteristics.
The aim of the programme is to monitor species composition, abundance and biomass of mesozooplankton. It provides data to monitoring strategy “SD1.6 Biodiversity – pelagic habitats”, as well as “SD2-Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptors D1, Criterion D1C6, Description D2 Criterions D2C1 and D2C2 and Descriptor D4 Criterion D4C2. Data are gathered to assess the state of the marine environment and environmental status in three coastal water bodies and all off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions) as well as pressures from/by non-indigenous species. Monitoring is conducted yearly with a frequency 10 times a year at the designated coastal monitoring stations (3 stations in each coastal water body) and with frequency twice a year for 16 stations in the Estonian off-shore areas. The program is regionally coordinated via HELCOM and the HELCOM guidelines are followed. Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). Mesozooplankton Mean Size Total Stock indicator is developed by HELCOM on the basis of mesozooplankton data. The threshold values for the indicator have been internationally agreed for some sub-basins, but not for the Gulf of Riga yet. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Pelagic habitats – community characteristics.
The aim of the programme is to monitor species composition, abundance and biomass of mesozooplankton. It provides data to monitoring strategy “SD1.6 Biodiversity – pelagic habitats”, as well as “SD2-Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptors D1, Criterion D1C6, Description D2 Criterions D2C1 and D2C2 and Descriptor D4 Criterion D4C2. Data are gathered to assess the state of the marine environment and environmental status in three coastal water bodies and all off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions) as well as pressures from/by non-indigenous species. Monitoring is conducted yearly with a frequency 10 times a year at the designated coastal monitoring stations (3 stations in each coastal water body) and with frequency twice a year for 16 stations in the Estonian off-shore areas. The program is regionally coordinated via HELCOM and the HELCOM guidelines are followed. Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). Mesozooplankton Mean Size Total Stock indicator is developed by HELCOM on the basis of mesozooplankton data. The threshold values for the indicator have been internationally agreed for some sub-basins, but not for the Gulf of Riga yet. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Pelagic habitats – community characteristics.
The aim of the programme is to monitor the occurrence and abundance/biomass of non-indigenous phytoplankton, zooplankton, macrozoobenthos and fish in harbours and adjacent areas. Port NIS monitoring is carried out in one port (Muuga) with the identified highest risk for introduction of new non-indigenous species, while monitoring of adjacent areas is performed for three harbours. In addition, species-specific monitoring covers a few most invasive non-indigenous species: the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. The programme provides data to monitoring strategy “SD2 – Non-indigenous species ”. The programme is primarily related to GES Descriptor D2, Criteria D2C1, D2C2 and D2C3; but also contributes to D1, D4 and D6. Monitoring is conducted annually at the designated monitoring stations with organism-group specific monitoring designs. The monitoring, data collection and assessment quality are assured by regional coordination via HELCOM, including following the OSPAR/HELCOM port biological monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March). The programme has been modified since 2014 by adding species-specific monitoring. The programme corresponds to the following monitoring programmes in the indicative list: Non-indigenous species inputs - from specific sources; Non-indigenous species - abundance and/or biomass.
The aim of the programme is to monitor the occurrence and abundance/biomass of non-indigenous phytoplankton, zooplankton, macrozoobenthos and fish in harbours and adjacent areas. Port NIS monitoring is carried out in one port (Muuga) with the identified highest risk for introduction of new non-indigenous species, while monitoring of adjacent areas is performed for three harbours. In addition, species-specific monitoring covers a few most invasive non-indigenous species: the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. The programme provides data to monitoring strategy “SD2 – Non-indigenous species ”. The programme is primarily related to GES Descriptor D2, Criteria D2C1, D2C2 and D2C3; but also contributes to D1, D4 and D6. Monitoring is conducted annually at the designated monitoring stations with organism-group specific monitoring designs. The monitoring, data collection and assessment quality are assured by regional coordination via HELCOM, including following the OSPAR/HELCOM port biological monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March). The programme has been modified since 2014 by adding species-specific monitoring. The programme corresponds to the following monitoring programmes in the indicative list: Non-indigenous species inputs - from specific sources; Non-indigenous species - abundance and/or biomass.
The aim of the programme is to monitor the occurrence and abundance/biomass of non-indigenous phytoplankton, zooplankton, macrozoobenthos and fish in harbours and adjacent areas. Port NIS monitoring is carried out in one port (Muuga) with the identified highest risk for introduction of new non-indigenous species, while monitoring of adjacent areas is performed for three harbours. In addition, species-specific monitoring covers a few most invasive non-indigenous species: the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. The programme provides data to monitoring strategy “SD2 – Non-indigenous species ”. The programme is primarily related to GES Descriptor D2, Criteria D2C1, D2C2 and D2C3; but also contributes to D1, D4 and D6. Monitoring is conducted annually at the designated monitoring stations with organism-group specific monitoring designs. The monitoring, data collection and assessment quality are assured by regional coordination via HELCOM, including following the OSPAR/HELCOM port biological monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March). The programme has been modified since 2014 by adding species-specific monitoring. The programme corresponds to the following monitoring programmes in the indicative list: Non-indigenous species inputs - from specific sources; Non-indigenous species - abundance and/or biomass.
The aim of the programme is to monitor the occurrence and abundance/biomass of non-indigenous phytoplankton, zooplankton, macrozoobenthos and fish in harbours and adjacent areas. Port NIS monitoring is carried out in one port (Muuga) with the identified highest risk for introduction of new non-indigenous species, while monitoring of adjacent areas is performed for three harbours. In addition, species-specific monitoring covers a few most invasive non-indigenous species: the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. The programme provides data to monitoring strategy “SD2 – Non-indigenous species ”. The programme is primarily related to GES Descriptor D2, Criteria D2C1, D2C2 and D2C3; but also contributes to D1, D4 and D6. Monitoring is conducted annually at the designated monitoring stations with organism-group specific monitoring designs. The monitoring, data collection and assessment quality are assured by regional coordination via HELCOM, including following the OSPAR/HELCOM port biological monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March). The programme has been modified since 2014 by adding species-specific monitoring. The programme corresponds to the following monitoring programmes in the indicative list: Non-indigenous species inputs - from specific sources; Non-indigenous species - abundance and/or biomass.
The aim of the programme is to cover all major organism groups (phyto/zooplankton, phyto/zoobenthos, fish) and monitor both, pelagic and benthic communities (abundance/biomass and proportion of non-indigenous species in zooplankton and macrozoobenthos communities, abundance/biomass of mobile species, and biopollution level index). Most of the data and information used originate from other monitoring strategies and programmes. The programme provides data to monitoring strategy “SD2 – Non-indigenous species ”. The programme is primarily related to GES Descriptor D2, Criteria D2C1, D2C2 and D2C3; but also contributes to D1, D4 and D6. Monitoring is conducted annually at the designated monitoring stations with organism-group specific monitoring designs. The assessment unit is the whole Estonian marine area. The monitoring and assessment quality is assured by regional coordination via HELCOM and following the HELCOM monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March). The threshold values for indicators required for MSFD assessments have been defined (nationally, except for the biopollution level). The programme corresponds to the following monitoring programmes in the indicative list: Non-indigenous species - abundance and/or biomass.
The aim of the programme is to cover all major organism groups (phyto/zooplankton, phyto/zoobenthos, fish) and monitor both, pelagic and benthic communities (abundance/biomass and proportion of non-indigenous species in zooplankton and macrozoobenthos communities, abundance/biomass of mobile species, and biopollution level index). Most of the data and information used originate from other monitoring strategies and programmes. The programme provides data to monitoring strategy “SD2 – Non-indigenous species ”. The programme is primarily related to GES Descriptor D2, Criteria D2C1, D2C2 and D2C3; but also contributes to D1, D4 and D6. Monitoring is conducted annually at the designated monitoring stations with organism-group specific monitoring designs. The assessment unit is the whole Estonian marine area. The monitoring and assessment quality is assured by regional coordination via HELCOM and following the HELCOM monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March). The threshold values for indicators required for MSFD assessments have been defined (nationally, except for the biopollution level). The programme corresponds to the following monitoring programmes in the indicative list: Non-indigenous species - abundance and/or biomass.
The aim of the programme is to monitor the surface accumulation of phytoplankton using remote sensing data. It provides data to monitoring strategy “SD5 – Eutrophication” and is related to GES Descriptor D5, Criterion D5C3. The status of mostly off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions) is assessed. Monitoring is conducted continuously. The program is regionally coordinated via HELCOM, and commonly developed and agreed algorithms are used. Algorithms and assessment methods (thresholds) are under development. The programme is essentially the same as in 2014, only minor changes: the satellites in use have been changed. The programme corresponds to the following monitoring programmes in the indicative list: Plankton blooms (biomass, frequency).
The aim of the programme is to monitor the surface accumulation of phytoplankton using remote sensing data. It provides data to monitoring strategy “SD5 – Eutrophication” and is related to GES Descriptor D5, Criterion D5C3. The status of mostly off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions) is assessed. Monitoring is conducted continuously. The program is regionally coordinated via HELCOM, and commonly developed and agreed algorithms are used. Algorithms and assessment methods (thresholds) are under development. The programme is essentially the same as in 2014, only minor changes: the satellites in use have been changed. The programme corresponds to the following monitoring programmes in the indicative list: Plankton blooms (biomass, frequency).
The aim of the programme is to monitor nutrient levels (total nitrogen, total phosphorus, NO3+NO2-N, NH4-N, PO4-P, SiO4-Si) in the water column. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD1.6 Biodiversity – pelagic habitats”. The programme is related to GES Descriptor D5, Criterion D5C1 and anthropogenic pressure “Input of nutrients” (MSFD Annex III). Data are gathered to assess the pressure levels in the marine environment and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions). Monitoring is conducted yearly or at least once in six years with a frequency of 6 to 12 times a year at the designated monitoring stations (at least 3 stations in each coastal water body and 18 in the Estonian off-shore areas). The programme data collection is regionally coordinated via HELCOM and the HELCOM guidelines are followed. The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and HELCOM ICES database (by 1 May). The threshold values for the indicators of concentrations of inorganic nitrogen and phosphorus in coastal waters have still to be developed. The programme is not designed to assess the internal and transboundary loads of nutrients. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Water column – chemical characteristics.
The aim of the programme is to monitor nutrient levels (total nitrogen, total phosphorus, NO3+NO2-N, NH4-N, PO4-P, SiO4-Si) in the water column. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD1.6 Biodiversity – pelagic habitats”. The programme is related to GES Descriptor D5, Criterion D5C1 and anthropogenic pressure “Input of nutrients” (MSFD Annex III). Data are gathered to assess the pressure levels in the marine environment and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions). Monitoring is conducted yearly or at least once in six years with a frequency of 6 to 12 times a year at the designated monitoring stations (at least 3 stations in each coastal water body and 18 in the Estonian off-shore areas). The programme data collection is regionally coordinated via HELCOM and the HELCOM guidelines are followed. The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and HELCOM ICES database (by 1 May). The threshold values for the indicators of concentrations of inorganic nitrogen and phosphorus in coastal waters have still to be developed. The programme is not designed to assess the internal and transboundary loads of nutrients. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Water column – chemical characteristics.
The aim of the programme is to monitor chemical characteristics in the water column (including near-bottom layer) to assess the indirect effects of eutrophication and describe conditions of the pelagic and benthic habitats. It provides data to monitoring strategy “SD5 – Eutrophication” and is related to GES Descriptor D5, Criterion D5C5. Data are gathered to assess the environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions). Monitoring is conducted yearly or at least once in six years with a frequency of 6 to 12 times a year at the designated monitoring stations (at least three stations in each coastal water body and 18 in the Estonian off-shore areas). The program data collection is regionally coordinated via HELCOM and the HELCOM guidelines are followed, but data are delivered separately by each country. Data are yearly reported to the environmental monitoring database KESE (by 1 March) and HELCOM ICES database (by 1 May). Monitoring of pCO2 is not continuous yet. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Water column – chemical characteristics.
The aim of the programme is to monitor chemical characteristics in the water column (including near-bottom layer) to assess the indirect effects of eutrophication and describe conditions of the pelagic and benthic habitats. It provides data to monitoring strategy “SD5 – Eutrophication” and is related to GES Descriptor D5, Criterion D5C5. Data are gathered to assess the environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions). Monitoring is conducted yearly or at least once in six years with a frequency of 6 to 12 times a year at the designated monitoring stations (at least three stations in each coastal water body and 18 in the Estonian off-shore areas). The program data collection is regionally coordinated via HELCOM and the HELCOM guidelines are followed, but data are delivered separately by each country. Data are yearly reported to the environmental monitoring database KESE (by 1 March) and HELCOM ICES database (by 1 May). Monitoring of pCO2 is not continuous yet. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Water column – chemical characteristics.
The aim of the programme is to monitor chemical characteristics in the water column (including near-bottom layer) to assess the indirect effects of eutrophication and describe conditions of the pelagic and benthic habitats. It provides data to monitoring strategy “SD5 – Eutrophication” and is related to GES Descriptor D5, Criterion D5C5. Data are gathered to assess the environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions). Monitoring is conducted yearly or at least once in six years with a frequency of 6 to 12 times a year at the designated monitoring stations (at least three stations in each coastal water body and 18 in the Estonian off-shore areas). The program data collection is regionally coordinated via HELCOM and the HELCOM guidelines are followed, but data are delivered separately by each country. Data are yearly reported to the environmental monitoring database KESE (by 1 March) and HELCOM ICES database (by 1 May). Monitoring of pCO2 is not continuous yet. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Water column – chemical characteristics.
The aim of the programme is to monitor physical characteristics (water temperature, salinity, transparency) in the water column to assess the indirect effects of eutrophication and describe the physical conditions of the pelagic habitats. It provides data to monitoring strategy “SD5 – Eutrophication” and is related to GES Descriptor D5, Criterion D5C4. Data are gathered to assess the environmental status in the coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions). Monitoring is conducted yearly or at least once in six years with a frequency of 6 to 12 times a year at the designated monitoring stations (at least three stations in each coastal water body and 18 in the Estonian off-shore areas). The program data collection is regionally coordinated via HELCOM and the HELCOM guidelines are followed, but data are delivered separately by each country (except CMEMS/BOOS monitoring with joint data collection). The data are yearly reported to the environmental monitoring database KESE (by 1 March), HELCOM ICES database (by 1 May) and online data delivery into CMEMS/BOOS databases. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Water column – physical characteristics.
The aim of the programme is to monitor physical characteristics (water temperature, salinity, transparency) in the water column to assess the indirect effects of eutrophication and describe the physical conditions of the pelagic habitats. It provides data to monitoring strategy “SD5 – Eutrophication” and is related to GES Descriptor D5, Criterion D5C4. Data are gathered to assess the environmental status in the coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions). Monitoring is conducted yearly or at least once in six years with a frequency of 6 to 12 times a year at the designated monitoring stations (at least three stations in each coastal water body and 18 in the Estonian off-shore areas). The program data collection is regionally coordinated via HELCOM and the HELCOM guidelines are followed, but data are delivered separately by each country (except CMEMS/BOOS monitoring with joint data collection). The data are yearly reported to the environmental monitoring database KESE (by 1 March), HELCOM ICES database (by 1 May) and online data delivery into CMEMS/BOOS databases. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Water column – physical characteristics.
The aim of the programme is to monitor physical characteristics (water temperature, salinity, transparency) in the water column to assess the indirect effects of eutrophication and describe the physical conditions of the pelagic habitats. It provides data to monitoring strategy “SD5 – Eutrophication” and is related to GES Descriptor D5, Criterion D5C4. Data are gathered to assess the environmental status in the coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions). Monitoring is conducted yearly or at least once in six years with a frequency of 6 to 12 times a year at the designated monitoring stations (at least three stations in each coastal water body and 18 in the Estonian off-shore areas). The program data collection is regionally coordinated via HELCOM and the HELCOM guidelines are followed, but data are delivered separately by each country (except CMEMS/BOOS monitoring with joint data collection). The data are yearly reported to the environmental monitoring database KESE (by 1 March), HELCOM ICES database (by 1 May) and online data delivery into CMEMS/BOOS databases. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Water column – physical characteristics.
The aim of the programme is to monitor physical characteristics (water temperature, salinity, transparency) in the water column to assess the indirect effects of eutrophication and describe the physical conditions of the pelagic habitats. It provides data to monitoring strategy “SD5 – Eutrophication” and is related to GES Descriptor D5, Criterion D5C4. Data are gathered to assess the environmental status in the coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions). Monitoring is conducted yearly or at least once in six years with a frequency of 6 to 12 times a year at the designated monitoring stations (at least three stations in each coastal water body and 18 in the Estonian off-shore areas). The program data collection is regionally coordinated via HELCOM and the HELCOM guidelines are followed, but data are delivered separately by each country (except CMEMS/BOOS monitoring with joint data collection). The data are yearly reported to the environmental monitoring database KESE (by 1 March), HELCOM ICES database (by 1 May) and online data delivery into CMEMS/BOOS databases. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Water column – physical characteristics.
The aim of the programme is to monitor physical characteristics (water temperature, salinity, transparency) in the water column to assess the indirect effects of eutrophication and describe the physical conditions of the pelagic habitats. It provides data to monitoring strategy “SD5 – Eutrophication” and is related to GES Descriptor D5, Criterion D5C4. Data are gathered to assess the environmental status in the coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions). Monitoring is conducted yearly or at least once in six years with a frequency of 6 to 12 times a year at the designated monitoring stations (at least three stations in each coastal water body and 18 in the Estonian off-shore areas). The program data collection is regionally coordinated via HELCOM and the HELCOM guidelines are followed, but data are delivered separately by each country (except CMEMS/BOOS monitoring with joint data collection). The data are yearly reported to the environmental monitoring database KESE (by 1 March), HELCOM ICES database (by 1 May) and online data delivery into CMEMS/BOOS databases. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Water column – physical characteristics.
The aim of the programme is to monitor physical characteristics (water temperature, salinity, transparency) in the water column to assess the indirect effects of eutrophication and describe the physical conditions of the pelagic habitats. It provides data to monitoring strategy “SD5 – Eutrophication” and is related to GES Descriptor D5, Criterion D5C4. Data are gathered to assess the environmental status in the coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions). Monitoring is conducted yearly or at least once in six years with a frequency of 6 to 12 times a year at the designated monitoring stations (at least three stations in each coastal water body and 18 in the Estonian off-shore areas). The program data collection is regionally coordinated via HELCOM and the HELCOM guidelines are followed, but data are delivered separately by each country (except CMEMS/BOOS monitoring with joint data collection). The data are yearly reported to the environmental monitoring database KESE (by 1 March), HELCOM ICES database (by 1 May) and online data delivery into CMEMS/BOOS databases. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Water column – physical characteristics.
The aim of the programme is to monitor physical characteristics (water temperature, salinity, transparency) in the water column to assess the indirect effects of eutrophication and describe the physical conditions of the pelagic habitats. It provides data to monitoring strategy “SD5 – Eutrophication” and is related to GES Descriptor D5, Criterion D5C4. Data are gathered to assess the environmental status in the coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions). Monitoring is conducted yearly or at least once in six years with a frequency of 6 to 12 times a year at the designated monitoring stations (at least three stations in each coastal water body and 18 in the Estonian off-shore areas). The program data collection is regionally coordinated via HELCOM and the HELCOM guidelines are followed, but data are delivered separately by each country (except CMEMS/BOOS monitoring with joint data collection). The data are yearly reported to the environmental monitoring database KESE (by 1 March), HELCOM ICES database (by 1 May) and online data delivery into CMEMS/BOOS databases. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Water column – physical characteristics.
The aim of the programme is to monitor hydrological characteristics in the marine areas to describe the physical/hydrological conditions of the benthic and pelagic habitats. Data on sea level, waves, and currents are acquired at sea, mostly using autonomous devices and numerical models. Both, coastal water bodies and the off-shore sub-basins of the Baltic Sea (HELCOM division) are monitored. Monitoring is conducted continuously. The program is regionally coordinated via BOOS and Baltic CMEMS (joint data collection). The data are delivered near real-time. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Water column – hydrological characteristics.
The aim of the programme is to monitor hydrological characteristics in the marine areas to describe the physical/hydrological conditions of the benthic and pelagic habitats. Data on sea level, waves, and currents are acquired at sea, mostly using autonomous devices and numerical models. Both, coastal water bodies and the off-shore sub-basins of the Baltic Sea (HELCOM division) are monitored. Monitoring is conducted continuously. The program is regionally coordinated via BOOS and Baltic CMEMS (joint data collection). The data are delivered near real-time. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Water column – hydrological characteristics.
The aim of the programme is to monitor hydrological characteristics in the marine areas to describe the physical/hydrological conditions of the benthic and pelagic habitats. Data on sea level, waves, and currents are acquired at sea, mostly using autonomous devices and numerical models. Both, coastal water bodies and the off-shore sub-basins of the Baltic Sea (HELCOM division) are monitored. Monitoring is conducted continuously. The program is regionally coordinated via BOOS and Baltic CMEMS (joint data collection). The data are delivered near real-time. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Water column – hydrological characteristics.
The aim of the programme is to monitor hydrological characteristics in the marine areas to describe the physical/hydrological conditions of the benthic and pelagic habitats. Data on sea level, waves, and currents are acquired at sea, mostly using autonomous devices and numerical models. Both, coastal water bodies and the off-shore sub-basins of the Baltic Sea (HELCOM division) are monitored. Monitoring is conducted continuously. The program is regionally coordinated via BOOS and Baltic CMEMS (joint data collection). The data are delivered near real-time. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Water column – hydrological characteristics.
The aim of the programme is to monitor hydrological characteristics in the marine areas to describe the physical/hydrological conditions of the benthic and pelagic habitats. Data on sea level, waves, and currents are acquired at sea, mostly using autonomous devices and numerical models. Both, coastal water bodies and the off-shore sub-basins of the Baltic Sea (HELCOM division) are monitored. Monitoring is conducted continuously. The program is regionally coordinated via BOOS and Baltic CMEMS (joint data collection). The data are delivered near real-time. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Water column – hydrological characteristics.
The aim of the programme is to monitor hydrological characteristics in the marine areas to describe the physical/hydrological conditions of the benthic and pelagic habitats. Data on sea level, waves, and currents are acquired at sea, mostly using autonomous devices and numerical models. Both, coastal water bodies and the off-shore sub-basins of the Baltic Sea (HELCOM division) are monitored. Monitoring is conducted continuously. The program is regionally coordinated via BOOS and Baltic CMEMS (joint data collection). The data are delivered near real-time. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Water column – hydrological characteristics.
The aim of the programme is to monitor characteristics of the ice cover. Data are collected by visual observations and remote sensing. Both, coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions) are monitored. Monitoring is conducted continuously during winter. The program is regionally coordinated (joint data collection) via Baltic Sea Ice Services and a common product is produced. The data are delivered daily. The programme corresponds to the following monitoring programmes in the indicative list: Ice cover.
Monitoring purpose
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Pressures in the marine environment
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Effectiveness of measures
  • Pressures in the marine environment
  • Effectiveness of measures
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
Other policies and conventions
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • Bathing Water Directive
  • Birds Directive
  • Convention on Long-Range Transboundary Air Pollution
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • IMO-BWM
  • Maritime Spatial Planning Directive
  • Minamata Convention on Mercury
  • Monitoring programme targeting at national legislation
  • National Emission Ceilings Directive
  • Nitrates Directive
  • Stockholm Convention on persistent organic pollutions (POPs)
  • Urban Waste Water Treatment Directive
  • Water Framework Directive
  • HELCOM Monitoring programmes
  • Monitoring programme targeting at national legislation
  • Water Framework Directive
  • HELCOM Monitoring programmes
  • Monitoring programme targeting at national legislation
  • Water Framework Directive
  • HELCOM Monitoring programmes
  • Monitoring programme targeting at national legislation
  • Water Framework Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Monitoring programme targeting at national legislation
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Monitoring programme targeting at national legislation
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Monitoring programme targeting at national legislation
  • Habitats Directive
  • IMO-BWM
  • Invasive Alien Species Regulation
  • Monitoring programme targeting at national legislation
  • Habitats Directive
  • IMO-BWM
  • Invasive Alien Species Regulation
  • Monitoring programme targeting at national legislation
  • Habitats Directive
  • IMO-BWM
  • Invasive Alien Species Regulation
  • Monitoring programme targeting at national legislation
  • Habitats Directive
  • IMO-BWM
  • Invasive Alien Species Regulation
  • Monitoring programme targeting at national legislation
  • Habitats Directive
  • IMO-BWM
  • Invasive Alien Species Regulation
  • Monitoring programme targeting at national legislation
  • Habitats Directive
  • IMO-BWM
  • Invasive Alien Species Regulation
  • Monitoring programme targeting at national legislation
  • Bathing Water Directive
  • Monitoring programme targeting at national legislation
  • Water Framework Directive
  • Bathing Water Directive
  • Monitoring programme targeting at national legislation
  • Water Framework Directive
  • Monitoring programme targeting at national legislation
  • Nitrates Directive
  • Water Framework Directive
  • Monitoring programme targeting at national legislation
  • Nitrates Directive
  • Water Framework Directive
  • Monitoring programme targeting at national legislation
  • Water Framework Directive
  • Monitoring programme targeting at national legislation
  • Water Framework Directive
  • Monitoring programme targeting at national legislation
  • Water Framework Directive
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Habitats Directive
  • Water Framework Directive
  • Habitats Directive
  • Water Framework Directive
  • Habitats Directive
  • Water Framework Directive
  • Habitats Directive
  • Water Framework Directive
  • Habitats Directive
  • Water Framework Directive
  • Habitats Directive
  • Water Framework Directive
  • Habitats Directive
  • Maritime Spatial Planning Directive
Regional cooperation - coordinating body
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • Other
Regional cooperation - countries involved
Regional cooperation - implementation level
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Joint data collection
Monitoring details
Phytoplankton samples are collected with a bathometer at water depths of 1, 5 and 10 m together with samples of seawater chlorophyll a. An integrated sample is made pooling equal amounts of water collected from fixed depths. When the integrated sample is thoroughly mixed, a portion is poured into a clear glass bottle and fixed with preservation chemical for further transport, storage and analysis of the phytoplankton sample. As part of the Ferrybox monitoring, samples are collected with an automatic sampler from depths of 4-5 m from a predefined location on the route of the liner. Phytoplankton is analysed according to the relevant international standard methods (EN 16695: 2015, HELCOM Monitoring Manual). In 3 coastal water bodies sampling is carried out annually 10-12 times per year (from April to October), Haapsalu coastal waterbody - 10-12 times every third year. Other coastal water bodies are monitored in rotation 6 times per year (from June to September) at least once during a 6-year period. In the off-shore areas the research vessel-based monitoring is conducted 5 times per year (from April to October) and 12 times every year in frames of Ferrybox monitoring.
Phytoplankton samples are collected with a bathometer at water depths of 1, 5 and 10 m together with samples of seawater chlorophyll a. An integrated sample is made pooling equal amounts of water collected from fixed depths. When the integrated sample is thoroughly mixed, a portion is poured into a clear glass bottle and fixed with preservation chemical for further transport, storage and analysis of the phytoplankton sample. As part of the Ferrybox monitoring, samples are collected with an automatic sampler from depths of 4-5 m from a predefined location on the route of the liner. Phytoplankton is analysed according to the relevant international standard methods (EN 16695: 2015, HELCOM Monitoring Manual). In 3 coastal water bodies sampling is carried out annually 10-12 times per year (from April to October), Haapsalu coastal waterbody - 10-12 times every third year. Other coastal water bodies are monitored in rotation 6 times per year (from June to September) at least once during a 6-year period. In the off-shore areas the research vessel-based monitoring is conducted 5 times per year (from April to October) and 12 times every year in frames of Ferrybox monitoring.
Phytoplankton samples are collected with a bathometer at water depths of 1, 5 and 10 m together with samples of seawater chlorophyll a. An integrated sample is made pooling equal amounts of water collected from fixed depths. When the integrated sample is thoroughly mixed, a portion is poured into a clear glass bottle and fixed with preservation chemical for further transport, storage and analysis of the phytoplankton sample. As part of the Ferrybox monitoring, samples are collected with an automatic sampler from depths of 4-5 m from a predefined location on the route of the liner. Phytoplankton is analysed according to the relevant international standard methods (EN 16695: 2015, HELCOM Monitoring Manual). In 3 coastal water bodies sampling is carried out annually 10-12 times per year (from April to October), Haapsalu coastal waterbody - 10-12 times every third year. Other coastal water bodies are monitored in rotation 6 times per year (from June to September) at least once during a 6-year period. In the off-shore areas the research vessel-based monitoring is conducted 5 times per year (from April to October) and 12 times every year in frames of Ferrybox monitoring.
The samples are collected by means of vertical hauls using a Juday or WP-2 net with 0,1 mm mesh size. The collected samples are preserved in a formaldehyde solution to microscopic analysis to be performed in a laboratory.
The samples are collected by means of vertical hauls using a Juday or WP-2 net with 0,1 mm mesh size. The collected samples are preserved in a formaldehyde solution to microscopic analysis to be performed in a laboratory.
The samples are collected by means of vertical hauls using a Juday or WP-2 net with 0,1 mm mesh size. The collected samples are preserved in a formaldehyde solution to microscopic analysis to be performed in a laboratory.
The phytoplankton, mesozooplankton, zoobenthos, fouling, mobile epifauna and fish monitoring samples are collected in accordance with HELCOM and HELCOM/OSPAR guidelines from two ports and three adjacent areas. Information on NIS occurrence is also gathered from all biological monitoring stations.
The phytoplankton, mesozooplankton, zoobenthos, fouling, mobile epifauna and fish monitoring samples are collected in accordance with HELCOM and HELCOM/OSPAR guidelines from two ports and three adjacent areas. Information on NIS occurrence is also gathered from all biological monitoring stations.
The phytoplankton, mesozooplankton, zoobenthos, fouling, mobile epifauna and fish monitoring samples are collected in accordance with HELCOM and HELCOM/OSPAR guidelines from two ports and three adjacent areas. Information on NIS occurrence is also gathered from all biological monitoring stations.
The phytoplankton, mesozooplankton, zoobenthos, fouling, mobile epifauna and fish monitoring samples are collected in accordance with HELCOM and HELCOM/OSPAR guidelines from two ports and three adjacent areas. Information on NIS occurrence is also gathered from all biological monitoring stations.
Most of the data and information used originate from other monitoring strategies and programmes. Information on NIS occurrence is gathered from all biological monitoring stations.
Most of the data and information used originate from other monitoring strategies and programmes. Information on NIS occurrence is gathered from all biological monitoring stations.
The monitoring and related indicator(s) are under development. Local applicable algorithms for Sentinel satellites data need to be developed.
The monitoring and related indicator(s) are under development. Local applicable algorithms for Sentinel satellites data need to be developed.
Samples are collected from designated monitoring stations with a bathometer at depths of 1, 5 and 10 m and near-bottom layer. As part of the Ferrybox monitoring, samples are collected with an automatic sampler from depths of 4-5 m from a predefined location on the route of the liner with installed equipment. Sampling is carried out annually up to 12 times per year (from June to September) at certain monitoring stations, and in rotation 6 times per year at least once in 6-year period at other monitoring stations. In the off-shore areas the monitoring is conducted 6 times per year and during winter cruise. In addition, samples are collected in frames of Ferrybox monitoring, 12 times every year in the period from April to October.
Samples are collected from designated monitoring stations with a bathometer at depths of 1, 5 and 10 m and near-bottom layer. As part of the Ferrybox monitoring, samples are collected with an automatic sampler from depths of 4-5 m from a predefined location on the route of the liner with installed equipment. Sampling is carried out annually up to 12 times per year (from June to September) at certain monitoring stations, and in rotation 6 times per year at least once in 6-year period at other monitoring stations. In the off-shore areas the monitoring is conducted 6 times per year and during winter cruise. In addition, samples are collected in frames of Ferrybox monitoring, 12 times every year in the period from April to October.
Dissolved oxygen concentration is measured at designated monitoring stations either in situ with CTD sonde oxygen sensors or in a laboratory from samples collected with a bathometer (surface layer and near-bottom layer). International guidelines are followed measuring H2S, pH and dissolved oxygen concentrations. H2S is measured at deepest monitoring stations in particular. Sampling is carried out annually up to 12 times per year (from June to September) at certain monitoring stations, and in rotation 6 times per year at least once in 6-year period at other monitoring stations. In the off-shore areas monitoring is conducted 6 times per year.
Dissolved oxygen concentration is measured at designated monitoring stations either in situ with CTD sonde oxygen sensors or in a laboratory from samples collected with a bathometer (surface layer and near-bottom layer). International guidelines are followed measuring H2S, pH and dissolved oxygen concentrations. H2S is measured at deepest monitoring stations in particular. Sampling is carried out annually up to 12 times per year (from June to September) at certain monitoring stations, and in rotation 6 times per year at least once in 6-year period at other monitoring stations. In the off-shore areas monitoring is conducted 6 times per year.
Dissolved oxygen concentration is measured at designated monitoring stations either in situ with CTD sonde oxygen sensors or in a laboratory from samples collected with a bathometer (surface layer and near-bottom layer). International guidelines are followed measuring H2S, pH and dissolved oxygen concentrations. H2S is measured at deepest monitoring stations in particular. Sampling is carried out annually up to 12 times per year (from June to September) at certain monitoring stations, and in rotation 6 times per year at least once in 6-year period at other monitoring stations. In the off-shore areas monitoring is conducted 6 times per year.
The temperature is measured within water column from surface to bottom with CTD sondes. Transparency is assessed with 30 cm diameter white Secchi disk. As part of the Ferrybox monitoring, the temperature and salinity are registered at depths of 4-5 m from a predefined location on the route of the liner with automatic equipment. CTD water column measurements of temperature and salinity are also being performed at autonomous monitoring buoys. Sampling is carried out annually up to 12 times per year (from June to September) at certain monitoring stations, and in rotation 6 times per year at least once in 6-year period at other monitoring stations. In the off-shore areas monitoring is conducted 6 times per year. Ferrybox, remote (satellite) measurements and measurements at autonomous buoys are being conducted continuously.
The temperature is measured within water column from surface to bottom with CTD sondes. Transparency is assessed with 30 cm diameter white Secchi disk. As part of the Ferrybox monitoring, the temperature and salinity are registered at depths of 4-5 m from a predefined location on the route of the liner with automatic equipment. CTD water column measurements of temperature and salinity are also being performed at autonomous monitoring buoys. Sampling is carried out annually up to 12 times per year (from June to September) at certain monitoring stations, and in rotation 6 times per year at least once in 6-year period at other monitoring stations. In the off-shore areas monitoring is conducted 6 times per year. Ferrybox, remote (satellite) measurements and measurements at autonomous buoys are being conducted continuously.
The temperature is measured within water column from surface to bottom with CTD sondes. Transparency is assessed with 30 cm diameter white Secchi disk. As part of the Ferrybox monitoring, the temperature and salinity are registered at depths of 4-5 m from a predefined location on the route of the liner with automatic equipment. CTD water column measurements of temperature and salinity are also being performed at autonomous monitoring buoys. Sampling is carried out annually up to 12 times per year (from June to September) at certain monitoring stations, and in rotation 6 times per year at least once in 6-year period at other monitoring stations. In the off-shore areas monitoring is conducted 6 times per year. Ferrybox, remote (satellite) measurements and measurements at autonomous buoys are being conducted continuously.
The temperature is measured within water column from surface to bottom with CTD sondes. Transparency is assessed with 30 cm diameter white Secchi disk. As part of the Ferrybox monitoring, the temperature and salinity are registered at depths of 4-5 m from a predefined location on the route of the liner with automatic equipment. CTD water column measurements of temperature and salinity are also being performed at autonomous monitoring buoys. Sampling is carried out annually up to 12 times per year (from June to September) at certain monitoring stations, and in rotation 6 times per year at least once in 6-year period at other monitoring stations. In the off-shore areas monitoring is conducted 6 times per year. Ferrybox, remote (satellite) measurements and measurements at autonomous buoys are being conducted continuously.
The temperature is measured within water column from surface to bottom with CTD sondes. Transparency is assessed with 30 cm diameter white Secchi disk. As part of the Ferrybox monitoring, the temperature and salinity are registered at depths of 4-5 m from a predefined location on the route of the liner with automatic equipment. CTD water column measurements of temperature and salinity are also being performed at autonomous monitoring buoys. Sampling is carried out annually up to 12 times per year (from June to September) at certain monitoring stations, and in rotation 6 times per year at least once in 6-year period at other monitoring stations. In the off-shore areas monitoring is conducted 6 times per year. Ferrybox, remote (satellite) measurements and measurements at autonomous buoys are being conducted continuously.
The temperature is measured within water column from surface to bottom with CTD sondes. Transparency is assessed with 30 cm diameter white Secchi disk. As part of the Ferrybox monitoring, the temperature and salinity are registered at depths of 4-5 m from a predefined location on the route of the liner with automatic equipment. CTD water column measurements of temperature and salinity are also being performed at autonomous monitoring buoys. Sampling is carried out annually up to 12 times per year (from June to September) at certain monitoring stations, and in rotation 6 times per year at least once in 6-year period at other monitoring stations. In the off-shore areas monitoring is conducted 6 times per year. Ferrybox, remote (satellite) measurements and measurements at autonomous buoys are being conducted continuously.
The temperature is measured within water column from surface to bottom with CTD sondes. Transparency is assessed with 30 cm diameter white Secchi disk. As part of the Ferrybox monitoring, the temperature and salinity are registered at depths of 4-5 m from a predefined location on the route of the liner with automatic equipment. CTD water column measurements of temperature and salinity are also being performed at autonomous monitoring buoys. Sampling is carried out annually up to 12 times per year (from June to September) at certain monitoring stations, and in rotation 6 times per year at least once in 6-year period at other monitoring stations. In the off-shore areas monitoring is conducted 6 times per year. Ferrybox, remote (satellite) measurements and measurements at autonomous buoys are being conducted continuously.
Monitoring is conducted at stations with automatic measurement equipment installed (water level, waves and currents measurements).
Monitoring is conducted at stations with automatic measurement equipment installed (water level, waves and currents measurements).
Monitoring is conducted at stations with automatic measurement equipment installed (water level, waves and currents measurements).
Monitoring is conducted at stations with automatic measurement equipment installed (water level, waves and currents measurements).
Monitoring is conducted at stations with automatic measurement equipment installed (water level, waves and currents measurements).
Monitoring is conducted at stations with automatic measurement equipment installed (water level, waves and currents measurements).
Ice monitoring is carried out as a part of national meteorological and hydrological monitoring (Estonian Environment Agency). Ice maps are produced in cooperation with Baltic Sea countries. TalTech Marine Systems Institute performs remote monitoring of ice on a project basis in cooperation with other Baltic Sea countries.
Features
Aquaculture – marine, including infrastructure
Fish and shellfish harvesting (professional, recreational)
Hunting and collecting for other purposes
Marine plant harvesting
Extraction of minerals (rock, metal ores, gravel, sand, shell)
Extraction of oil and gas, including infrastructure
Extraction of water
Military operations (subject to Article 2(2))
Transmission of electricity and communications (cables)
Renewable energy generation (wind, wave and tidal power), including infrastructure
Research, survey and educational activities
Coastal defence and flood protection
Offshore structures (other than for oil/gas/renewables)
Restructuring of seabed morphology, including dredging and depositing of materials
Tourism and leisure activities
Tourism and leisure infrastructure
Transport infrastructure
Transport – shipping
Waste treatment and disposal
Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) – diffuse sources, point sources, atmospheric deposition, acute events
Input of litter (solid waste matter, including micro-sized litter)
Input of nutrients – diffuse sources, point sources, atmospheric deposition
Input of anthropogenic sound (impulsive, continuous)
Other pelagic habitats
Coastal ecosystems
Coastal ecosystems
Other pelagic habitats
Coastal ecosystems
Coastal ecosystems
Newly introduced non-indigenous species
Established non-indigenous species
Established non-indigenous species
Established non-indigenous species
Newly introduced non-indigenous species
Established non-indigenous species
Pelagic broad habitats
Eutrophication
Eutrophication
Chemical characteristics
Eutrophication
Eutrophication
Chemical characteristics
Eutrophication
Physical and hydrological characteristics
Physical and hydrological characteristics
Physical and hydrological characteristics
Hydrographical changes
Hydrographical changes
Hydrographical changes
Physical and hydrological characteristics
Physical and hydrological characteristics
Physical and hydrological characteristics
Hydrographical changes
Hydrographical changes
Hydrographical changes
Physical and hydrological characteristics
Elements
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Not Applicable
  • Phytoplankton communities
  • Primary producers
  • Primary producers
  • Zooplankton communities
  • All trophic guilds
  • Secondary producers
  • All trophic guilds
  • Secondary producers
  • Not Applicable
  • Benthic habitats - macrobenthic communities
  • Benthic habitats - macrophyte communities
  • Zooplankton communities
  • Eriocheir sinensis
  • Neogobius melanostomus
  • Rhithropanopeus harrisii
  • Fouling
  • Mobile epifauna
  • Phytoplankton communities
  • Not Applicable
  • Eriocheir sinensis
  • Neogobius melanostomus
  • Rhithropanopeus harrisii
  • Coastal pelagic habitat
  • Cyanobacteria
  • Maximum concentration of blooming species
  • DIP
  • NH4+
  • NO2-N
  • NO3-N
  • Silicate (SiO4)
  • TN
  • TP
  • DIP
  • NH4+
  • NO2-N
  • NO3-N
  • Silicate (SiO4)
  • TN
  • TP
  • Hydrogen sulfide (H2S)
  • Dissolved oxygen (O2)
  • Dissolved oxygen (O2)
  • H2S
  • pH
  • Transparency
  • Salinity
  • Temperature
  • Transparency
  • Salinity
  • Temperature
  • Transparency
  • Current regime
  • Sea level
  • Wave regime
  • Current regime
  • Sea level
  • Wave regime
  • Ice
GES criteria
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
D1C6
D4C1
D4C2
D1C6
D4C1
D4C2
D2C1
D2C2
D2C2
D2C2
D2C1
D2C2
D1C6
D5C3
D5C1
NotRelevan
D5C1
D5C5
NotRelevan
D5C4
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
NotRelevan
Parameters
  • Other
  • Other
  • Other
  • Other
  • Other
  • Other
  • Other
  • Other
  • Other
  • Other
  • Other
  • Other
  • Other
  • Other
  • Other
  • Other
  • Other
  • Other
  • Other
  • Other
  • AMO-WC
  • Amount on coastline
  • Amount on seabed
  • Other
  • Other
  • Level of sound
  • Other
  • Other
  • Other
  • Abundance (number of individuals)
  • Biomass
  • Other
  • Other
  • Abundance (number of individuals)
  • Biomass
  • Other
  • Abundance (number of individuals)
  • Biomass
  • Other
  • Abundance (number of individuals)
  • Biomass
  • Abundance (number of individuals)
  • Biomass
  • Other
  • Other
  • Abundance (number of individuals)
  • Biomass
  • Extent
  • Other
  • Duration
  • Extent
  • Frequency
  • Concentration in water
  • Concentration in water
  • Concentration in water
  • Concentration in water
  • Concentration in water
  • Transparency of water
  • Salinity
  • Temperature
  • Transparency of water
  • Salinity
  • Temperature
  • Transparency of water
  • Current velocity
  • Other
  • Other
  • Other
  • Current velocity
  • Other
  • Other
  • Other
  • Other
Parameter Other
Production (tonnes); Area; Nutrient load
Catch; By-catch
Number of individuals hunted by species (waterbird
Amount (kg); Area
Mining volume; Mining area; Area pressure index
Pipe length (area); Area pressure index
Volume
Number of explosions; Number of trainings; Trainin
Cable length (area); Area pressure index
Area; Area pressure index
Volume of costs on marine researches; Number of re
Length of defence structure; Coastline pressure in
Area of structure; Area pressure index
Soil volume; Extent; Area pressure index
Number of vacationists; Number of visits; People's
Number of marinas per coastline; Length of beach
Area; Volume (goods and passengers); Number of loa
Number of ships (incl. number of ships complying w
Areas of dumping sites and volume of dumped materi
Pollution load (tonnes/year) - Hg, Cd, Cu, Pb, Zn,
Amount in sediments; Litter type and material
Pollution load (tonnes/year) - N, P, BHT5
Number of disturbance days - Impulsive underwater
Species composition; Abundance (number of individu
Species composition
Species composition; Abundance (number of individu
Species composition
Species composition; Abundance (number of individu
Species composition; Relative biomass in community
Species composition
Species composition; Abundance (number of individu
Species composition
Number of bloom events and duration
Direction
Water level
Significant wave height; Period; Direction
Direction
Water level
Significant wave height; Period; Direction
Extent; Thickness; Concentration; Ice type
Spatial scope
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
Marine reporting units
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_05
  • BAL-GR-EE-EEEE_13
  • BAL-EE-AA
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_05
  • BAL-GR-EE-EEEE_13
  • BAL-EE-AA
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_05
  • BAL-GR-EE-EEEE_13
  • BAL-EE-AA
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_05
  • BAL-GR-EE-EEEE_13
  • BAL-EE-AA
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_05
  • BAL-GR-EE-EEEE_13
  • BAL-EE-AA
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_05
  • BAL-GR-EE-EEEE_13
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB
  • BAL-EE-GF
  • BAL-EE-GR
  • BAL-EE-NBP
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB-OFFSHORE
  • BAL-EE-GF-OFFSHORE
  • BAL-EE-GR-OFFSHORE
  • BAL-EE-NBP-OFFSHORE
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB-OFFSHORE
  • BAL-EE-GF-OFFSHORE
  • BAL-EE-GR-OFFSHORE
  • BAL-EE-NBP-OFFSHORE
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB-OFFSHORE
  • BAL-EE-GF-OFFSHORE
  • BAL-EE-GR-OFFSHORE
  • BAL-EE-NBP-OFFSHORE
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB-OFFSHORE
  • BAL-EE-GF-OFFSHORE
  • BAL-EE-GR-OFFSHORE
  • BAL-EE-NBP-OFFSHORE
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB-OFFSHORE
  • BAL-EE-GF-OFFSHORE
  • BAL-EE-GR-OFFSHORE
  • BAL-EE-NBP-OFFSHORE
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB-OFFSHORE
  • BAL-EE-GF-OFFSHORE
  • BAL-EE-GR-OFFSHORE
  • BAL-EE-NBP-OFFSHORE
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB-OFFSHORE
  • BAL-EE-GF-OFFSHORE
  • BAL-EE-GR-OFFSHORE
  • BAL-EE-NBP-OFFSHORE
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB-OFFSHORE
  • BAL-EE-GF-OFFSHORE
  • BAL-EE-GR-OFFSHORE
  • BAL-EE-NBP-OFFSHORE
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB-OFFSHORE
  • BAL-EE-GF-OFFSHORE
  • BAL-EE-GR-OFFSHORE
  • BAL-EE-NBP-OFFSHORE
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB-OFFSHORE
  • BAL-EE-GF-OFFSHORE
  • BAL-EE-GR-OFFSHORE
  • BAL-EE-NBP-OFFSHORE
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB-OFFSHORE
  • BAL-EE-GF-OFFSHORE
  • BAL-EE-GR-OFFSHORE
  • BAL-EE-NBP-OFFSHORE
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB-OFFSHORE
  • BAL-EE-GF-OFFSHORE
  • BAL-EE-GR-OFFSHORE
  • BAL-EE-NBP-OFFSHORE
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB-OFFSHORE
  • BAL-EE-GF-OFFSHORE
  • BAL-EE-GR-OFFSHORE
  • BAL-EE-NBP-OFFSHORE
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB-OFFSHORE
  • BAL-EE-GF-OFFSHORE
  • BAL-EE-GR-OFFSHORE
  • BAL-EE-NBP-OFFSHORE
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB-OFFSHORE
  • BAL-EE-GF-OFFSHORE
  • BAL-EE-GR-OFFSHORE
  • BAL-EE-NBP-OFFSHORE
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB-OFFSHORE
  • BAL-EE-GF-OFFSHORE
  • BAL-EE-GR-OFFSHORE
  • BAL-EE-NBP-OFFSHORE
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB-OFFSHORE
  • BAL-EE-GF-OFFSHORE
  • BAL-EE-GR-OFFSHORE
  • BAL-EE-NBP-OFFSHORE
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB-OFFSHORE
  • BAL-EE-GF-OFFSHORE
  • BAL-EE-GR-OFFSHORE
  • BAL-EE-NBP-OFFSHORE
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
  • BAL-EE-AA
  • BAL-EE-EGB-OFFSHORE
  • BAL-EE-GF-OFFSHORE
  • BAL-EE-GR-OFFSHORE
  • BAL-EE-NBP-OFFSHORE
  • BAL-EGB-EE-EEEE_11
  • BAL-GF-EE-EEEE_01
  • BAL-GF-EE-EEEE_02
  • BAL-GF-EE-EEEE_03
  • BAL-GF-EE-EEEE_05
  • BAL-GF-EE-EEEE_06
  • BAL-GR-EE-EEEE_07
  • BAL-GR-EE-EEEE_08
  • BAL-GR-EE-EEEE_09
  • BAL-GR-EE-EEEE_13
  • BAL-GR-EE-EEEE_14
  • BAL-GR-EE-EEEE_16
  • BAL-GR-EE-EEEE_17
  • BAL-GR-EE-EEEE_18
  • BAL-GR-EE-EEEE_19
  • BAL-NBP-EE-EEEE_10
Temporal scope (start date - end date)
2015-9999
2015-9999
2015-9999
2015-9999
2015-9999
2015-9999
2015-9999
2015-9999
2015-9999
2015-9999
2015-9999
2015-9999
2015-9999
2015-9999
2015-9999
2015-9999
2015-9999
2015-9999
2015-9999
2015-9999
2015-9999
2015-9999
2015-9999
1993-9999
1993-9999
1993-9999
1993-9999
1993-9999
1993-9999
2010-9999
2010-9999
2010-9999
2010-9999
2010-9999
2010-9999
2006-9999
2006-9999
1993-9999
1993-9999
1993-9999
1993-9999
1993-9999
1993-9999
1993-9999
1993-9999
1993-9999
1993-9999
1993-9999
1993-9999
1993-9999
1993-9999
1993-9999
1993-9999
1993-9999
1993-9999
2007-9999
Monitoring frequency
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Other
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Other
Other
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Continually
Continually
Continually
Continually
Continually
Continually
Continually
Monitoring type
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • 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 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
  • Numerical modelling
  • In-situ sampling coastal
  • Numerical modelling
  • Remote satellite imagery
  • Remote satellite imagery
  • 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 offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • Remote satellite imagery
  • Remote surveillance
  • In-situ sampling coastal
  • In-situ sampling offshore
  • Remote satellite imagery
  • Remote surveillance
  • In-situ sampling coastal
  • In-situ sampling offshore
  • Remote satellite imagery
  • Remote surveillance
  • In-situ sampling coastal
  • In-situ sampling offshore
  • Remote satellite imagery
  • Remote surveillance
  • In-situ sampling coastal
  • In-situ sampling offshore
  • Remote satellite imagery
  • Remote surveillance
  • In-situ sampling coastal
  • In-situ sampling offshore
  • Remote satellite imagery
  • Remote surveillance
  • In-situ sampling coastal
  • In-situ sampling offshore
  • Remote satellite imagery
  • Remote surveillance
  • In-situ sampling coastal
  • Numerical modelling
  • Remote satellite imagery
  • Remote surveillance
  • In-situ sampling coastal
  • Numerical modelling
  • Remote satellite imagery
  • Remote surveillance
  • In-situ sampling coastal
  • Numerical modelling
  • Remote satellite imagery
  • Remote surveillance
  • In-situ sampling coastal
  • Numerical modelling
  • Remote satellite imagery
  • Remote surveillance
  • In-situ sampling coastal
  • Numerical modelling
  • Remote satellite imagery
  • Remote surveillance
  • In-situ sampling coastal
  • Numerical modelling
  • Remote satellite imagery
  • Remote surveillance
  • Numerical modelling
  • Remote satellite imagery
  • Visual observation
Monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region
  • Other monitoring method
  • HELCOM Guidelines for monitoring phytoplankton species composition, abundance and biomass
  • HELCOM Guidelines for monitoring phytoplankton species composition, abundance and biomass
  • HELCOM Guidelines for monitoring phytoplankton species composition, abundance and biomass
  • HELCOM Guidelines for monitoring of mesozooplankton
  • HELCOM Guidelines for monitoring of mesozooplankton
  • HELCOM Guidelines for monitoring of mesozooplankton
  • HELCOM Guidelines for monitoring of mesozooplankton
  • HELCOM Guidelines for monitoring of non-indigenous species by eRAS
  • HELCOM Guidelines for monitoring phytoplankton species composition, abundance and biomass
  • OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06)
  • Other monitoring method
  • HELCOM Guidelines for monitoring of mesozooplankton
  • HELCOM Guidelines for monitoring of non-indigenous species by eRAS
  • HELCOM Guidelines for monitoring phytoplankton species composition, abundance and biomass
  • OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06)
  • Other monitoring method
  • HELCOM Guidelines for monitoring of mesozooplankton
  • HELCOM Guidelines for monitoring of non-indigenous species by eRAS
  • HELCOM Guidelines for monitoring phytoplankton species composition, abundance and biomass
  • OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06)
  • Other monitoring method
  • HELCOM Guidelines for monitoring of mesozooplankton
  • HELCOM Guidelines for monitoring of non-indigenous species by eRAS
  • HELCOM Guidelines for monitoring phytoplankton species composition, abundance and biomass
  • OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06)
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • HELCOM Guidelines for sampling and determination of ammonium
  • HELCOM Guidelines for sampling and determination of nitrate
  • HELCOM Guidelines for sampling and determination of nitrite
  • HELCOM Guidelines for sampling and determination of phosphate
  • HELCOM Guidelines for sampling and determination of silicate
  • HELCOM Guidelines for sampling and determination of total nitrogen
  • HELCOM Guidelines for sampling and determination of total phosphorus
  • HELCOM Guidelines for sampling and determination of ammonium
  • HELCOM Guidelines for sampling and determination of nitrate
  • HELCOM Guidelines for sampling and determination of nitrite
  • HELCOM Guidelines for sampling and determination of phosphate
  • HELCOM Guidelines for sampling and determination of silicate
  • HELCOM Guidelines for sampling and determination of total nitrogen
  • HELCOM Guidelines for sampling and determination of total phosphorus
  • HELCOM Guidelines for sampling and determination of dissolved oxygen
  • HELCOM Guidelines for sampling and determination of hydrogen sulphide
  • HELCOM Guidelines for sampling and determination of pH
  • HELCOM Guidelines for sampling and determination of dissolved oxygen
  • HELCOM Guidelines for sampling and determination of hydrogen sulphide
  • HELCOM Guidelines for sampling and determination of pH
  • HELCOM Guidelines for sampling and determination of dissolved oxygen
  • HELCOM Guidelines for sampling and determination of hydrogen sulphide
  • HELCOM Guidelines for sampling and determination of pH
  • HELCOM Guidelines for determination of salinity and temperature using CTD
  • HELCOM Guidelines for measuring Secchi depth
  • HELCOM Guidelines for determination of salinity and temperature using CTD
  • HELCOM Guidelines for measuring Secchi depth
  • HELCOM Guidelines for determination of salinity and temperature using CTD
  • HELCOM Guidelines for measuring Secchi depth
  • HELCOM Guidelines for determination of salinity and temperature using CTD
  • HELCOM Guidelines for measuring Secchi depth
  • HELCOM Guidelines for determination of salinity and temperature using CTD
  • HELCOM Guidelines for measuring Secchi depth
  • HELCOM Guidelines for determination of salinity and temperature using CTD
  • HELCOM Guidelines for measuring Secchi depth
  • HELCOM Guidelines for determination of salinity and temperature using CTD
  • HELCOM Guidelines for measuring Secchi depth
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
Monitoring method other
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.
Joint HELCOM/OSPAR Guidelines on the granting of exemptions under the International Convention for the Control and Management of Ships’ Ballast Water and Sediments, Regulation A (https://www.helcom.fi/wp-content/uploads/2019/08/Joint-HELCOM_OSPAR-Guidelines.pdf);
Joint HELCOM/OSPAR Guidelines on the granting of exemptions under the International Convention for the Control and Management of Ships’ Ballast Water and Sediments, Regulation A (https://www.helcom.fi/wp-content/uploads/2019/08/Joint-HELCOM_OSPAR-Guidelines.pdf);
Joint HELCOM/OSPAR Guidelines on the granting of exemptions under the International Convention for the Control and Management of Ships’ Ballast Water and Sediments, Regulation A (https://www.helcom.fi/wp-content/uploads/2019/08/Joint-HELCOM_OSPAR-Guidelines.pdf);
Joint HELCOM/OSPAR Guidelines on the granting of exemptions under the International Convention for the Control and Management of Ships’ Ballast Water and Sediments, Regulation A (https://www.helcom.fi/wp-content/uploads/2019/08/Joint-HELCOM_OSPAR-Guidelines.pdf);
The numerical data used are calculated on the basis of data collected under other programmes. The level of biopollution is assessed on the basis of a scientifically validated methodology (Olenin et al. 2007) for an average of three sub-basins (the Gulf of Riga, the Gulf of Finland and the Baltic Proper).
The numerical data used are calculated on the basis of data collected under other programmes. The level of biopollution is assessed on the basis of a scientifically validated methodology (Olenin et al. 2007) for an average of three sub-basins (the Gulf of Riga, the Gulf of Finland and the Baltic Proper).
National, under development
National, under development
Automatic measurements and mathematical modelling - Copernicus marine service (http://marine.copernicus.eu/) and BOOS (http://www.boos.org/).
Automatic measurements and mathematical modelling - Copernicus marine service (http://marine.copernicus.eu/) and BOOS (http://www.boos.org/).
Automatic measurements and mathematical modelling - Copernicus marine service (http://marine.copernicus.eu/) and BOOS (http://www.boos.org/).
Automatic measurements and mathematical modelling - Copernicus marine service (http://marine.copernicus.eu/) and BOOS (http://www.boos.org/).
Automatic measurements and mathematical modelling - Copernicus marine service (http://marine.copernicus.eu/) and BOOS (http://www.boos.org/).
Automatic measurements and mathematical modelling - Copernicus marine service (http://marine.copernicus.eu/) and BOOS (http://www.boos.org/).
The main characteristics of ice cover are measured using satellite observations or/and in combination - satellite images and visual observations.
Quality control
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
Data quality control systems of relevant data sources.
The quality is ensured by following the standard methods and HELCOM guidance as well as accreditation of experts and persons by whom the monitoring is performed.
The quality is ensured by following the standard methods and HELCOM guidance as well as accreditation of experts and persons by whom the monitoring is performed.
The quality is ensured by following the standard methods and HELCOM guidance as well as accreditation of experts and persons by whom the monitoring is performed.
The quality is ensured by following the HELCOM guidance as well as accreditation of experts and persons by whom the monitoring is performed.
The quality is ensured by following the HELCOM guidance as well as accreditation of experts and persons by whom the monitoring is performed.
The quality is ensured by following the HELCOM guidance as well as accreditation of experts and persons by whom the monitoring is performed.
The quality is ensured by the accreditation of experts and persons by whom the monitoring is performed and following guidance recommendations.
The quality is ensured by the accreditation of experts and persons by whom the monitoring is performed and following guidance recommendations.
The quality is ensured by the accreditation of experts and persons by whom the monitoring is performed and following guidance recommendations.
The quality is ensured by the accreditation of experts and persons by whom the monitoring is performed and following guidance recommendations.
The monitoring and assessment quality is assured by regional coordination via HELCOM, following the HELCOM, HELCOM/OSPAR and national monitoring guidelines, and accreditation of experts and persons by whom the monitoring is performed.
The monitoring and assessment quality is assured by regional coordination via HELCOM, following the HELCOM, HELCOM/OSPAR and national monitoring guidelines, and accreditation of experts and persons by whom the monitoring is performed.
The quality is assured by using regionally developed algorithms and by international collaboration.
The quality is assured by using regionally developed algorithms and by international collaboration.
The quality is assured by following the standard methods and HELCOM guidelines, by an accreditation of experts and persons by whom the monitoring is performed and filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025.
The quality is assured by following the standard methods and HELCOM guidelines, by an accreditation of experts and persons by whom the monitoring is performed and filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025.
The quality is assured by following the standards (ISO 5814, EVS-EN ISO 10523) and HELCOM guidelines and CMEMS protocols, by an accreditation of experts and persons by whom the monitoring is performed.
The quality is assured by following the standards (ISO 5814, EVS-EN ISO 10523) and HELCOM guidelines and CMEMS protocols, by an accreditation of experts and persons by whom the monitoring is performed.
The quality is assured by following the standards (ISO 5814, EVS-EN ISO 10523) and HELCOM guidelines and CMEMS protocols, by an accreditation of experts and persons by whom the monitoring is performed.
The quality is assured by following international standards, including CMEMS protocols and HELCOM guidelines, and by an accreditation of experts and persons by whom the monitoring is performed.
The quality is assured by following international standards, including CMEMS protocols and HELCOM guidelines, and by an accreditation of experts and persons by whom the monitoring is performed.
The quality is assured by following international standards, including CMEMS protocols and HELCOM guidelines, and by an accreditation of experts and persons by whom the monitoring is performed.
The quality is assured by following international standards, including CMEMS protocols and HELCOM guidelines, and by an accreditation of experts and persons by whom the monitoring is performed.
The quality is assured by following international standards, including CMEMS protocols and HELCOM guidelines, and by an accreditation of experts and persons by whom the monitoring is performed.
The quality is assured by following international standards, including CMEMS protocols and HELCOM guidelines, and by an accreditation of experts and persons by whom the monitoring is performed.
The quality is assured by following international standards, including CMEMS protocols and HELCOM guidelines, and by an accreditation of experts and persons by whom the monitoring is performed.
The quality is assured by following WMO guidelines (weather service); operational measurements and mathematical modelling are in compliance with Copernicus maritime service quality system.
The quality is assured by following WMO guidelines (weather service); operational measurements and mathematical modelling are in compliance with Copernicus maritime service quality system.
The quality is assured by following WMO guidelines (weather service); operational measurements and mathematical modelling are in compliance with Copernicus maritime service quality system.
The quality is assured by following WMO guidelines (weather service); operational measurements and mathematical modelling are in compliance with Copernicus maritime service quality system.
The quality is assured by following WMO guidelines (weather service); operational measurements and mathematical modelling are in compliance with Copernicus maritime service quality system.
The quality is assured by following WMO guidelines (weather service); operational measurements and mathematical modelling are in compliance with Copernicus maritime service quality system.
WMO and CMEMS quality assurance system (Cal/Val).
Data management
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.
Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine).
Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine).
Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine).
Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine).
Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine).
Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine).
Data are yearly reported to the national environmental monitoring database KESE (by 1 March).
Data are yearly reported to the national environmental monitoring database KESE (by 1 March).
Data are yearly reported to the national environmental monitoring database KESE (by 1 March).
Data are yearly reported to the national environmental monitoring database KESE (by 1 March).
The data are yearly reported to the national environmental monitoring database KESE (by 1 March).
The data are yearly reported to the national environmental monitoring database KESE (by 1 March).
Raw data (excl satellite images) are stored at the national environmental monitoring database KESE.
Raw data (excl satellite images) are stored at the national environmental monitoring database KESE.
The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine).
The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine).
The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine).
The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine).
The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine).
The data are yearly reported to the national environmental monitoring database KESE (by 1 March). The data on autonomous buoys measurements are stored at CMEMS/EMODnet Physics.
The data are yearly reported to the national environmental monitoring database KESE (by 1 March). The data on autonomous buoys measurements are stored at CMEMS/EMODnet Physics.
The data are yearly reported to the national environmental monitoring database KESE (by 1 March). The data on autonomous buoys measurements are stored at CMEMS/EMODnet Physics.
The data are yearly reported to the national environmental monitoring database KESE (by 1 March). The data on autonomous buoys measurements are stored at CMEMS/EMODnet Physics.
The data are yearly reported to the national environmental monitoring database KESE (by 1 March). The data on autonomous buoys measurements are stored at CMEMS/EMODnet Physics.
The data are yearly reported to the national environmental monitoring database KESE (by 1 March). The data on autonomous buoys measurements are stored at CMEMS/EMODnet Physics.
The data are yearly reported to the national environmental monitoring database KESE (by 1 March). The data on autonomous buoys measurements are stored at CMEMS/EMODnet Physics.
The data are stored at Estonian Environment Agency (Weather Service) in WISKI database, TalTech Marine Systems Institute (BOOS) and CMEMS in situ data. Automatic measurements and modelled data are available through Copernicus Marine Service and/or EMODnet Physics.
The data are stored at Estonian Environment Agency (Weather Service) in WISKI database, TalTech Marine Systems Institute (BOOS) and CMEMS in situ data. Automatic measurements and modelled data are available through Copernicus Marine Service and/or EMODnet Physics.
The data are stored at Estonian Environment Agency (Weather Service) in WISKI database, TalTech Marine Systems Institute (BOOS) and CMEMS in situ data. Automatic measurements and modelled data are available through Copernicus Marine Service and/or EMODnet Physics.
The data are stored at Estonian Environment Agency (Weather Service) in WISKI database, TalTech Marine Systems Institute (BOOS) and CMEMS in situ data. Automatic measurements and modelled data are available through Copernicus Marine Service and/or EMODnet Physics.
The data are stored at Estonian Environment Agency (Weather Service) in WISKI database, TalTech Marine Systems Institute (BOOS) and CMEMS in situ data. Automatic measurements and modelled data are available through Copernicus Marine Service and/or EMODnet Physics.
The data are stored at Estonian Environment Agency (Weather Service) in WISKI database, TalTech Marine Systems Institute (BOOS) and CMEMS in situ data. Automatic measurements and modelled data are available through Copernicus Marine Service and/or EMODnet Physics.
The data are stored at Estonian Environment Agency, TalTech Marine Systems Institute (http://sahm.ttu.ee/balticseapic/index.php?do=ice) and Baltic Sea Ice Services (http://www.bsis-ice.de/).
Data access
http://register.keskkonnainfo.ee/envreg/main#HTTPMEaW1ThSjHUyzXzMt7jr3MuRYp5PuE,https://andmed.stat.ee/et/stat,https://geoportaal.maaamet.ee/,https://kese.envir.ee,https://kotkas.envir.ee/,https://veeteedeamet.ee/et/laevandus-eesti-lipp-sadamad/eesti-laevaregistrid,https://vet.agri.ee/et/kalandus-toiduturg/puugistatistika-lossimiskohad-ja-kala-esmakokkuostukohad/puugiandmed,https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.eas.ee/teenused/,https://www.ehr.ee/,https://www.envir.ee/et/eesmargid-tegevused/kalandus/harrastuspuuk/statistika-ja-uuringud,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded,https://www.etis.ee/,https://www.keskkonnaagentuur.ee/et/kuttimine,https://www.keskkonnaamet.ee/et/eesmargid-tegevused/jahindus/operatiivsed-kuttimisandmed,https://www.marinetraffic.com/en/ais/,https://www.sadamaregister.ee/,https://www.terviseamet.ee/et/keskkonnatervis/ettevotjale-ja-kohalikule-omavalitsusele/supluskohad-ja-ujulad/suplusvee-profiilid,https://xgis.maaamet.ee/xgis2/page/app/maainfo,https://xgis.maaamet.ee/xgis2/page/app/merekaart
http://register.keskkonnainfo.ee/envreg/main#HTTPMEaW1ThSjHUyzXzMt7jr3MuRYp5PuE,https://andmed.stat.ee/et/stat,https://geoportaal.maaamet.ee/,https://kese.envir.ee,https://kotkas.envir.ee/,https://veeteedeamet.ee/et/laevandus-eesti-lipp-sadamad/eesti-laevaregistrid,https://vet.agri.ee/et/kalandus-toiduturg/puugistatistika-lossimiskohad-ja-kala-esmakokkuostukohad/puugiandmed,https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.eas.ee/teenused/,https://www.ehr.ee/,https://www.envir.ee/et/eesmargid-tegevused/kalandus/harrastuspuuk/statistika-ja-uuringud,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded,https://www.etis.ee/,https://www.keskkonnaagentuur.ee/et/kuttimine,https://www.keskkonnaamet.ee/et/eesmargid-tegevused/jahindus/operatiivsed-kuttimisandmed,https://www.marinetraffic.com/en/ais/,https://www.sadamaregister.ee/,https://www.terviseamet.ee/et/keskkonnatervis/ettevotjale-ja-kohalikule-omavalitsusele/supluskohad-ja-ujulad/suplusvee-profiilid,https://xgis.maaamet.ee/xgis2/page/app/maainfo,https://xgis.maaamet.ee/xgis2/page/app/merekaart
http://register.keskkonnainfo.ee/envreg/main#HTTPMEaW1ThSjHUyzXzMt7jr3MuRYp5PuE,https://andmed.stat.ee/et/stat,https://geoportaal.maaamet.ee/,https://kese.envir.ee,https://kotkas.envir.ee/,https://veeteedeamet.ee/et/laevandus-eesti-lipp-sadamad/eesti-laevaregistrid,https://vet.agri.ee/et/kalandus-toiduturg/puugistatistika-lossimiskohad-ja-kala-esmakokkuostukohad/puugiandmed,https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.eas.ee/teenused/,https://www.ehr.ee/,https://www.envir.ee/et/eesmargid-tegevused/kalandus/harrastuspuuk/statistika-ja-uuringud,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded,https://www.etis.ee/,https://www.keskkonnaagentuur.ee/et/kuttimine,https://www.keskkonnaamet.ee/et/eesmargid-tegevused/jahindus/operatiivsed-kuttimisandmed,https://www.marinetraffic.com/en/ais/,https://www.sadamaregister.ee/,https://www.terviseamet.ee/et/keskkonnatervis/ettevotjale-ja-kohalikule-omavalitsusele/supluskohad-ja-ujulad/suplusvee-profiilid,https://xgis.maaamet.ee/xgis2/page/app/maainfo,https://xgis.maaamet.ee/xgis2/page/app/merekaart
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http://register.keskkonnainfo.ee/envreg/main#HTTPMEaW1ThSjHUyzXzMt7jr3MuRYp5PuE,https://andmed.stat.ee/et/stat,https://geoportaal.maaamet.ee/,https://kese.envir.ee,https://kotkas.envir.ee/,https://veeteedeamet.ee/et/laevandus-eesti-lipp-sadamad/eesti-laevaregistrid,https://vet.agri.ee/et/kalandus-toiduturg/puugistatistika-lossimiskohad-ja-kala-esmakokkuostukohad/puugiandmed,https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.eas.ee/teenused/,https://www.ehr.ee/,https://www.envir.ee/et/eesmargid-tegevused/kalandus/harrastuspuuk/statistika-ja-uuringud,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded,https://www.etis.ee/,https://www.keskkonnaagentuur.ee/et/kuttimine,https://www.keskkonnaamet.ee/et/eesmargid-tegevused/jahindus/operatiivsed-kuttimisandmed,https://www.marinetraffic.com/en/ais/,https://www.sadamaregister.ee/,https://www.terviseamet.ee/et/keskkonnatervis/ettevotjale-ja-kohalikule-omavalitsusele/supluskohad-ja-ujulad/suplusvee-profiilid,https://xgis.maaamet.ee/xgis2/page/app/maainfo,https://xgis.maaamet.ee/xgis2/page/app/merekaart
http://register.keskkonnainfo.ee/envreg/main#HTTPMEaW1ThSjHUyzXzMt7jr3MuRYp5PuE,https://andmed.stat.ee/et/stat,https://geoportaal.maaamet.ee/,https://kese.envir.ee,https://kotkas.envir.ee/,https://veeteedeamet.ee/et/laevandus-eesti-lipp-sadamad/eesti-laevaregistrid,https://vet.agri.ee/et/kalandus-toiduturg/puugistatistika-lossimiskohad-ja-kala-esmakokkuostukohad/puugiandmed,https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.eas.ee/teenused/,https://www.ehr.ee/,https://www.envir.ee/et/eesmargid-tegevused/kalandus/harrastuspuuk/statistika-ja-uuringud,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded,https://www.etis.ee/,https://www.keskkonnaagentuur.ee/et/kuttimine,https://www.keskkonnaamet.ee/et/eesmargid-tegevused/jahindus/operatiivsed-kuttimisandmed,https://www.marinetraffic.com/en/ais/,https://www.sadamaregister.ee/,https://www.terviseamet.ee/et/keskkonnatervis/ettevotjale-ja-kohalikule-omavalitsusele/supluskohad-ja-ujulad/suplusvee-profiilid,https://xgis.maaamet.ee/xgis2/page/app/maainfo,https://xgis.maaamet.ee/xgis2/page/app/merekaart
http://register.keskkonnainfo.ee/envreg/main#HTTPMEaW1ThSjHUyzXzMt7jr3MuRYp5PuE,https://andmed.stat.ee/et/stat,https://geoportaal.maaamet.ee/,https://kese.envir.ee,https://kotkas.envir.ee/,https://veeteedeamet.ee/et/laevandus-eesti-lipp-sadamad/eesti-laevaregistrid,https://vet.agri.ee/et/kalandus-toiduturg/puugistatistika-lossimiskohad-ja-kala-esmakokkuostukohad/puugiandmed,https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.eas.ee/teenused/,https://www.ehr.ee/,https://www.envir.ee/et/eesmargid-tegevused/kalandus/harrastuspuuk/statistika-ja-uuringud,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded,https://www.etis.ee/,https://www.keskkonnaagentuur.ee/et/kuttimine,https://www.keskkonnaamet.ee/et/eesmargid-tegevused/jahindus/operatiivsed-kuttimisandmed,https://www.marinetraffic.com/en/ais/,https://www.sadamaregister.ee/,https://www.terviseamet.ee/et/keskkonnatervis/ettevotjale-ja-kohalikule-omavalitsusele/supluskohad-ja-ujulad/suplusvee-profiilid,https://xgis.maaamet.ee/xgis2/page/app/maainfo,https://xgis.maaamet.ee/xgis2/page/app/merekaart
http://register.keskkonnainfo.ee/envreg/main#HTTPMEaW1ThSjHUyzXzMt7jr3MuRYp5PuE,https://andmed.stat.ee/et/stat,https://geoportaal.maaamet.ee/,https://kese.envir.ee,https://kotkas.envir.ee/,https://veeteedeamet.ee/et/laevandus-eesti-lipp-sadamad/eesti-laevaregistrid,https://vet.agri.ee/et/kalandus-toiduturg/puugistatistika-lossimiskohad-ja-kala-esmakokkuostukohad/puugiandmed,https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.eas.ee/teenused/,https://www.ehr.ee/,https://www.envir.ee/et/eesmargid-tegevused/kalandus/harrastuspuuk/statistika-ja-uuringud,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded,https://www.etis.ee/,https://www.keskkonnaagentuur.ee/et/kuttimine,https://www.keskkonnaamet.ee/et/eesmargid-tegevused/jahindus/operatiivsed-kuttimisandmed,https://www.marinetraffic.com/en/ais/,https://www.sadamaregister.ee/,https://www.terviseamet.ee/et/keskkonnatervis/ettevotjale-ja-kohalikule-omavalitsusele/supluskohad-ja-ujulad/suplusvee-profiilid,https://xgis.maaamet.ee/xgis2/page/app/maainfo,https://xgis.maaamet.ee/xgis2/page/app/merekaart
http://register.keskkonnainfo.ee/envreg/main#HTTPMEaW1ThSjHUyzXzMt7jr3MuRYp5PuE,https://andmed.stat.ee/et/stat,https://geoportaal.maaamet.ee/,https://kese.envir.ee,https://kotkas.envir.ee/,https://veeteedeamet.ee/et/laevandus-eesti-lipp-sadamad/eesti-laevaregistrid,https://vet.agri.ee/et/kalandus-toiduturg/puugistatistika-lossimiskohad-ja-kala-esmakokkuostukohad/puugiandmed,https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.eas.ee/teenused/,https://www.ehr.ee/,https://www.envir.ee/et/eesmargid-tegevused/kalandus/harrastuspuuk/statistika-ja-uuringud,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded,https://www.etis.ee/,https://www.keskkonnaagentuur.ee/et/kuttimine,https://www.keskkonnaamet.ee/et/eesmargid-tegevused/jahindus/operatiivsed-kuttimisandmed,https://www.marinetraffic.com/en/ais/,https://www.sadamaregister.ee/,https://www.terviseamet.ee/et/keskkonnatervis/ettevotjale-ja-kohalikule-omavalitsusele/supluskohad-ja-ujulad/suplusvee-profiilid,https://xgis.maaamet.ee/xgis2/page/app/maainfo,https://xgis.maaamet.ee/xgis2/page/app/merekaart
http://register.keskkonnainfo.ee/envreg/main#HTTPMEaW1ThSjHUyzXzMt7jr3MuRYp5PuE,https://andmed.stat.ee/et/stat,https://geoportaal.maaamet.ee/,https://kese.envir.ee,https://kotkas.envir.ee/,https://veeteedeamet.ee/et/laevandus-eesti-lipp-sadamad/eesti-laevaregistrid,https://vet.agri.ee/et/kalandus-toiduturg/puugistatistika-lossimiskohad-ja-kala-esmakokkuostukohad/puugiandmed,https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.eas.ee/teenused/,https://www.ehr.ee/,https://www.envir.ee/et/eesmargid-tegevused/kalandus/harrastuspuuk/statistika-ja-uuringud,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded,https://www.etis.ee/,https://www.keskkonnaagentuur.ee/et/kuttimine,https://www.keskkonnaamet.ee/et/eesmargid-tegevused/jahindus/operatiivsed-kuttimisandmed,https://www.marinetraffic.com/en/ais/,https://www.sadamaregister.ee/,https://www.terviseamet.ee/et/keskkonnatervis/ettevotjale-ja-kohalikule-omavalitsusele/supluskohad-ja-ujulad/suplusvee-profiilid,https://xgis.maaamet.ee/xgis2/page/app/maainfo,https://xgis.maaamet.ee/xgis2/page/app/merekaart
http://register.keskkonnainfo.ee/envreg/main#HTTPMEaW1ThSjHUyzXzMt7jr3MuRYp5PuE,https://andmed.stat.ee/et/stat,https://geoportaal.maaamet.ee/,https://kese.envir.ee,https://kotkas.envir.ee/,https://veeteedeamet.ee/et/laevandus-eesti-lipp-sadamad/eesti-laevaregistrid,https://vet.agri.ee/et/kalandus-toiduturg/puugistatistika-lossimiskohad-ja-kala-esmakokkuostukohad/puugiandmed,https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.eas.ee/teenused/,https://www.ehr.ee/,https://www.envir.ee/et/eesmargid-tegevused/kalandus/harrastuspuuk/statistika-ja-uuringud,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded,https://www.etis.ee/,https://www.keskkonnaagentuur.ee/et/kuttimine,https://www.keskkonnaamet.ee/et/eesmargid-tegevused/jahindus/operatiivsed-kuttimisandmed,https://www.marinetraffic.com/en/ais/,https://www.sadamaregister.ee/,https://www.terviseamet.ee/et/keskkonnatervis/ettevotjale-ja-kohalikule-omavalitsusele/supluskohad-ja-ujulad/suplusvee-profiilid,https://xgis.maaamet.ee/xgis2/page/app/maainfo,https://xgis.maaamet.ee/xgis2/page/app/merekaart
http://register.keskkonnainfo.ee/envreg/main#HTTPMEaW1ThSjHUyzXzMt7jr3MuRYp5PuE,https://andmed.stat.ee/et/stat,https://geoportaal.maaamet.ee/,https://kese.envir.ee,https://kotkas.envir.ee/,https://veeteedeamet.ee/et/laevandus-eesti-lipp-sadamad/eesti-laevaregistrid,https://vet.agri.ee/et/kalandus-toiduturg/puugistatistika-lossimiskohad-ja-kala-esmakokkuostukohad/puugiandmed,https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.eas.ee/teenused/,https://www.ehr.ee/,https://www.envir.ee/et/eesmargid-tegevused/kalandus/harrastuspuuk/statistika-ja-uuringud,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded,https://www.etis.ee/,https://www.keskkonnaagentuur.ee/et/kuttimine,https://www.keskkonnaamet.ee/et/eesmargid-tegevused/jahindus/operatiivsed-kuttimisandmed,https://www.marinetraffic.com/en/ais/,https://www.sadamaregister.ee/,https://www.terviseamet.ee/et/keskkonnatervis/ettevotjale-ja-kohalikule-omavalitsusele/supluskohad-ja-ujulad/suplusvee-profiilid,https://xgis.maaamet.ee/xgis2/page/app/maainfo,https://xgis.maaamet.ee/xgis2/page/app/merekaart
http://register.keskkonnainfo.ee/envreg/main#HTTPMEaW1ThSjHUyzXzMt7jr3MuRYp5PuE,https://andmed.stat.ee/et/stat,https://geoportaal.maaamet.ee/,https://kese.envir.ee,https://kotkas.envir.ee/,https://veeteedeamet.ee/et/laevandus-eesti-lipp-sadamad/eesti-laevaregistrid,https://vet.agri.ee/et/kalandus-toiduturg/puugistatistika-lossimiskohad-ja-kala-esmakokkuostukohad/puugiandmed,https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.eas.ee/teenused/,https://www.ehr.ee/,https://www.envir.ee/et/eesmargid-tegevused/kalandus/harrastuspuuk/statistika-ja-uuringud,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded,https://www.etis.ee/,https://www.keskkonnaagentuur.ee/et/kuttimine,https://www.keskkonnaamet.ee/et/eesmargid-tegevused/jahindus/operatiivsed-kuttimisandmed,https://www.marinetraffic.com/en/ais/,https://www.sadamaregister.ee/,https://www.terviseamet.ee/et/keskkonnatervis/ettevotjale-ja-kohalikule-omavalitsusele/supluskohad-ja-ujulad/suplusvee-profiilid,https://xgis.maaamet.ee/xgis2/page/app/maainfo,https://xgis.maaamet.ee/xgis2/page/app/merekaart
http://register.keskkonnainfo.ee/envreg/main#HTTPMEaW1ThSjHUyzXzMt7jr3MuRYp5PuE,https://andmed.stat.ee/et/stat,https://geoportaal.maaamet.ee/,https://kese.envir.ee,https://kotkas.envir.ee/,https://veeteedeamet.ee/et/laevandus-eesti-lipp-sadamad/eesti-laevaregistrid,https://vet.agri.ee/et/kalandus-toiduturg/puugistatistika-lossimiskohad-ja-kala-esmakokkuostukohad/puugiandmed,https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.eas.ee/teenused/,https://www.ehr.ee/,https://www.envir.ee/et/eesmargid-tegevused/kalandus/harrastuspuuk/statistika-ja-uuringud,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded,https://www.etis.ee/,https://www.keskkonnaagentuur.ee/et/kuttimine,https://www.keskkonnaamet.ee/et/eesmargid-tegevused/jahindus/operatiivsed-kuttimisandmed,https://www.marinetraffic.com/en/ais/,https://www.sadamaregister.ee/,https://www.terviseamet.ee/et/keskkonnatervis/ettevotjale-ja-kohalikule-omavalitsusele/supluskohad-ja-ujulad/suplusvee-profiilid,https://xgis.maaamet.ee/xgis2/page/app/maainfo,https://xgis.maaamet.ee/xgis2/page/app/merekaart
Related indicator/name
Contact
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
References
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).
The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).