MS/Art11/2020/D6/Estonia/Baltic Sea

Member State report / Art11 / 2020 / D6 / 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	D6 Sea-floor integrity/D1 Benthic habitats
Member State	Estonia
Region/subregion	Baltic Sea
Reported by	Estonian Environment Agency
Report date	2020-11-11
Report access	ART11_Programmes_Merge_EE_v5.xml msfd-ART11_Strategies_ea.xml

Simplified table

Descriptor	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1	D6/D1
Monitoring strategy description	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".	The aim of the monitoring strategy “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” is to assess the status of benthic habitats by collecting data on the condition of benthic communities, species distribution, distribution and status of benthic habitats and extent as well as effect of human-induced disturbances to the seafloor. The following monitoring programmes produce data for the assessments of the status and impact as well as pressures in the environment: "Seabed habitats – community characteristics", "Phytobenthic communities", "Seabed physical and chemical characteristics", "Macrozoobenthos", "Physical loss and disturbance – from different human activities", "Water column – chemical characteristics", "Water column – physical characteristics", "Hydrological characteristics", "Coasts", "Marine and coastal activities".
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Gaps and plans	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.	Data on human activities causing physical loss and disturbance to the seabed are insufficiently georeferenced or missing, i.e information on environmental permits and respective works are available, but data on activities' actual locations and their extent are not inserted to the GIS-database. It is necessary to organise the process of harvesting data on activities related to environmental permits and ensure GIS-data availability. The number of monitoring stations and benthic transects in coastal waters is not sufficient to provide high-level confidence assessments of the ecological status of a body of water in some areas. There is no regular monitoring of the Habitats Directive habitat types yet, providing input to broad habitat type assessments, only project-based researches are carried out. The methodology was developed in frames of project NEMA. There is neither zoobenthos transect in the Northern Baltic Proper nor Limecola balthica depth distribution monitoring, thus the status can't be assessed there (lacking an indicator to assess circalittoral habitat types in NBP). Deep-water oxygen levels should be measured at least at 2-3 stations in the Eastern Gotland Basin (lacking an indicator for assessment of circalittoral habitat types). The protected areas monitoring programme needs to be developed and include birds, mammals, fish, benthos, and habitats, as well as pelagic communities' components. The use of remote sensing methods to monitor seabed habitats in the shallow sea will be taken into consideration.
Related targets	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19	BALEE-T30 BALEE-T34 Target 19
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	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-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'	BALEE-M001 - 'Developing a network of MPA in the Estonian EEZ' BALEE-M002 - 'Compiling regional aquaculture plans to manage environmental pressures' Not specified - 'Establishing maritime spatial plans and implementing the HELCOM Recommendation 28E/9' Not specified - 'Estonian Environmental Strategy 2030' Not specified - 'The development of a network of protected areas in the coastal and territorial sea of the Baltic Sea'
Coverage of measures	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024	Adequate monitoring will be in place by 2024
Related monitoring programmes	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010406-12_SeabedHabitat BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D01040607-15_SeabedPhysChemGeol BALEE-D01040607-16_PhysDisturb BALEE-D05-24_WaterColumnChem BALEE-D0507-25_WaterColumnPhys BALEE-D07-26_PhysCharWaves BALEE-D07-28_SeaCoast
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-D010406-12_SeabedHabitat	BALEE-D010406-12_SeabedHabitat	BALEE-D010406-12_SeabedHabitat	BALEE-D01040605-13_SeabedVegetationZone	BALEE-D01040605-13_SeabedVegetationZone	BALEE-D01040605-13_SeabedVegetationZone	BALEE-D01040605-13_SeabedVegetationZone	BALEE-D01040605-13_SeabedVegetationZone	BALEE-D01040605-13_SeabedVegetationZone	BALEE-D01040605-14_Macrozoobenthos	BALEE-D01040605-14_Macrozoobenthos	BALEE-D01040605-14_Macrozoobenthos	BALEE-D01040605-14_Macrozoobenthos	BALEE-D01040605-14_Macrozoobenthos	BALEE-D01040605-14_Macrozoobenthos	BALEE-D01040605-14_Macrozoobenthos	BALEE-D01040605-14_Macrozoobenthos	BALEE-D01040605-14_Macrozoobenthos	BALEE-D01040607-15_SeabedPhysChemGeol	BALEE-D01040607-15_SeabedPhysChemGeol	BALEE-D01040607-15_SeabedPhysChemGeol	BALEE-D01040607-15_SeabedPhysChemGeol	BALEE-D01040607-16_PhysDisturb	BALEE-D01040607-16_PhysDisturb	BALEE-D01040607-16_PhysDisturb	BALEE-D01040607-16_PhysDisturb	BALEE-D01040607-16_PhysDisturb	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-D07-28_SeaCoast	BALEE-D07-28_SeaCoast	BALEE-D07-28_SeaCoast	BALEE-D07-28_SeaCoast
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	Seabed habitats – community characteristics	Seabed habitats – community characteristics	Seabed habitats – community characteristics	Phytobenthic communities	Phytobenthic communities	Phytobenthic communities	Phytobenthic communities	Phytobenthic communities	Phytobenthic communities	Macrozoobenthos	Macrozoobenthos	Macrozoobenthos	Macrozoobenthos	Macrozoobenthos	Macrozoobenthos	Macrozoobenthos	Macrozoobenthos	Macrozoobenthos	Seabed physical and chemical characteristics	Seabed physical and chemical characteristics	Seabed physical and chemical characteristics	Seabed physical and chemical characteristics	Physical loss and disturbance – from different human activities	Physical loss and disturbance – from different human activities	Physical loss and disturbance – from different human activities	Physical loss and disturbance – from different human activities	Physical loss and disturbance – from different human activities	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	Coasts	Coasts	Coasts	Coasts
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	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	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	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-D010406-12_SeabedHabitat BALEE-D010406-17_ComStockFurcellaria	BALEE-D010406-12_SeabedHabitat BALEE-D010406-17_ComStockFurcellaria	BALEE-D010406-12_SeabedHabitat BALEE-D010406-17_ComStockFurcellaria																				BALEE-D01040607-16_PhysDisturb	BALEE-D01040607-16_PhysDisturb	BALEE-D01040607-16_PhysDisturb	BALEE-D01040607-16_PhysDisturb	BALEE-D01040607-16_PhysDisturb
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 the status of benthic habitats (presence, distribution, abundance, biomass of the species; characteristics of the sediment and near-bottom water layer; distribution characteristics of loose Furcellaria lumbricalis community). It provides data to monitoring strategy „SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats“ as well as “SD5 – Eutrophication”. The programme is related to GES Descriptor D6, Criterion D6C5; Descriptor D5 Criterions D5C5, D5C7 and D5C8. 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 sub-divisions) in response to pressure levels. Monitoring is conducted yearly, bi-annually or at least once in six years with a frequency of once a year at the designated monitoring stations. The program is partly regionally coordinated via HELCOM (soft-bottom habitats) and the HELCOM monitoring manual is followed conducting certain elements of the programme. Data are reported to the national environmental monitoring database KESE and ICES (HELCOM Combine). The programme has been changed since 2014 by adding the part about the commercial stock of Furcellaria lumbricalis (former sub-programme BALEE-D010406-17_ComStockFurcellaria). The programme corresponds to the following monitoring programmes in the indicative list: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass; Seabed habitats - distribution and extent.	The aim of the programme is to monitor the status of benthic habitats (presence, distribution, abundance, biomass of the species; characteristics of the sediment and near-bottom water layer; distribution characteristics of loose Furcellaria lumbricalis community). It provides data to monitoring strategy „SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats“ as well as “SD5 – Eutrophication”. The programme is related to GES Descriptor D6, Criterion D6C5; Descriptor D5 Criterions D5C5, D5C7 and D5C8. 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 sub-divisions) in response to pressure levels. Monitoring is conducted yearly, bi-annually or at least once in six years with a frequency of once a year at the designated monitoring stations. The program is partly regionally coordinated via HELCOM (soft-bottom habitats) and the HELCOM monitoring manual is followed conducting certain elements of the programme. Data are reported to the national environmental monitoring database KESE and ICES (HELCOM Combine). The programme has been changed since 2014 by adding the part about the commercial stock of Furcellaria lumbricalis (former sub-programme BALEE-D010406-17_ComStockFurcellaria). The programme corresponds to the following monitoring programmes in the indicative list: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass; Seabed habitats - distribution and extent.	The aim of the programme is to monitor the status of benthic habitats (presence, distribution, abundance, biomass of the species; characteristics of the sediment and near-bottom water layer; distribution characteristics of loose Furcellaria lumbricalis community). It provides data to monitoring strategy „SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats“ as well as “SD5 – Eutrophication”. The programme is related to GES Descriptor D6, Criterion D6C5; Descriptor D5 Criterions D5C5, D5C7 and D5C8. 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 sub-divisions) in response to pressure levels. Monitoring is conducted yearly, bi-annually or at least once in six years with a frequency of once a year at the designated monitoring stations. The program is partly regionally coordinated via HELCOM (soft-bottom habitats) and the HELCOM monitoring manual is followed conducting certain elements of the programme. Data are reported to the national environmental monitoring database KESE and ICES (HELCOM Combine). The programme has been changed since 2014 by adding the part about the commercial stock of Furcellaria lumbricalis (former sub-programme BALEE-D010406-17_ComStockFurcellaria). The programme corresponds to the following monitoring programmes in the indicative list: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass; Seabed habitats - distribution and extent.	The aim of the programme is to monitor phytobenthic communities (species composition, coverage, abundance, biomass, depth distribution) along the depth gradient. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” and “SD2– Non-indigenous species”. The programme is related to GES Descriptor D5, Criterion D5C6 and Criterion D5C7, Descriptor D6, Criterion D6C5. 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 sub-divisions) in response to pressure levels. Monitoring is conducted in coastal waters yearly or at least once per six years with a frequency once a year at the designated monitoring stations (at least 3 stations in each coastal water body). The program is regionally partly coordinated via HELCOM and the HELCOM monitoring manual is followed (soft-bottom habitats). Data are yearly reported to the national environmental monitoring database KESE (by 1 March). The programme corresponds to the following monitoring programmes in the indicative list: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass.	The aim of the programme is to monitor phytobenthic communities (species composition, coverage, abundance, biomass, depth distribution) along the depth gradient. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” and “SD2– Non-indigenous species”. The programme is related to GES Descriptor D5, Criterion D5C6 and Criterion D5C7, Descriptor D6, Criterion D6C5. 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 sub-divisions) in response to pressure levels. Monitoring is conducted in coastal waters yearly or at least once per six years with a frequency once a year at the designated monitoring stations (at least 3 stations in each coastal water body). The program is regionally partly coordinated via HELCOM and the HELCOM monitoring manual is followed (soft-bottom habitats). Data are yearly reported to the national environmental monitoring database KESE (by 1 March). The programme corresponds to the following monitoring programmes in the indicative list: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass.	The aim of the programme is to monitor phytobenthic communities (species composition, coverage, abundance, biomass, depth distribution) along the depth gradient. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” and “SD2– Non-indigenous species”. The programme is related to GES Descriptor D5, Criterion D5C6 and Criterion D5C7, Descriptor D6, Criterion D6C5. 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 sub-divisions) in response to pressure levels. Monitoring is conducted in coastal waters yearly or at least once per six years with a frequency once a year at the designated monitoring stations (at least 3 stations in each coastal water body). The program is regionally partly coordinated via HELCOM and the HELCOM monitoring manual is followed (soft-bottom habitats). Data are yearly reported to the national environmental monitoring database KESE (by 1 March). The programme corresponds to the following monitoring programmes in the indicative list: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass.	The aim of the programme is to monitor phytobenthic communities (species composition, coverage, abundance, biomass, depth distribution) along the depth gradient. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” and “SD2– Non-indigenous species”. The programme is related to GES Descriptor D5, Criterion D5C6 and Criterion D5C7, Descriptor D6, Criterion D6C5. 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 sub-divisions) in response to pressure levels. Monitoring is conducted in coastal waters yearly or at least once per six years with a frequency once a year at the designated monitoring stations (at least 3 stations in each coastal water body). The program is regionally partly coordinated via HELCOM and the HELCOM monitoring manual is followed (soft-bottom habitats). Data are yearly reported to the national environmental monitoring database KESE (by 1 March). The programme corresponds to the following monitoring programmes in the indicative list: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass.	The aim of the programme is to monitor phytobenthic communities (species composition, coverage, abundance, biomass, depth distribution) along the depth gradient. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” and “SD2– Non-indigenous species”. The programme is related to GES Descriptor D5, Criterion D5C6 and Criterion D5C7, Descriptor D6, Criterion D6C5. 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 sub-divisions) in response to pressure levels. Monitoring is conducted in coastal waters yearly or at least once per six years with a frequency once a year at the designated monitoring stations (at least 3 stations in each coastal water body). The program is regionally partly coordinated via HELCOM and the HELCOM monitoring manual is followed (soft-bottom habitats). Data are yearly reported to the national environmental monitoring database KESE (by 1 March). The programme corresponds to the following monitoring programmes in the indicative list: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass.	The aim of the programme is to monitor phytobenthic communities (species composition, coverage, abundance, biomass, depth distribution) along the depth gradient. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” and “SD2– Non-indigenous species”. The programme is related to GES Descriptor D5, Criterion D5C6 and Criterion D5C7, Descriptor D6, Criterion D6C5. 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 sub-divisions) in response to pressure levels. Monitoring is conducted in coastal waters yearly or at least once per six years with a frequency once a year at the designated monitoring stations (at least 3 stations in each coastal water body). The program is regionally partly coordinated via HELCOM and the HELCOM monitoring manual is followed (soft-bottom habitats). Data are yearly reported to the national environmental monitoring database KESE (by 1 March). The programme corresponds to the following monitoring programmes in the indicative list: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass.	The aim of the programme is to monitor macrozoobenthos communities (species composition, abundance and biomass) on the seafloor. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats”, “SD2– Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptor D5, Criterion D5C8, Descriptor D2, Criteria D2C1, D2C2 and D2C3, Descriptor D4, Criterion D4C2 and Descriptor D6, Criterion D6C5. 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 division) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency once 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. The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). 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: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass.	The aim of the programme is to monitor macrozoobenthos communities (species composition, abundance and biomass) on the seafloor. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats”, “SD2– Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptor D5, Criterion D5C8, Descriptor D2, Criteria D2C1, D2C2 and D2C3, Descriptor D4, Criterion D4C2 and Descriptor D6, Criterion D6C5. 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 division) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency once 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. The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). 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: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass.	The aim of the programme is to monitor macrozoobenthos communities (species composition, abundance and biomass) on the seafloor. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats”, “SD2– Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptor D5, Criterion D5C8, Descriptor D2, Criteria D2C1, D2C2 and D2C3, Descriptor D4, Criterion D4C2 and Descriptor D6, Criterion D6C5. 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 division) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency once 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. The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). 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: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass.	The aim of the programme is to monitor macrozoobenthos communities (species composition, abundance and biomass) on the seafloor. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats”, “SD2– Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptor D5, Criterion D5C8, Descriptor D2, Criteria D2C1, D2C2 and D2C3, Descriptor D4, Criterion D4C2 and Descriptor D6, Criterion D6C5. 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 division) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency once 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. The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). 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: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass.	The aim of the programme is to monitor macrozoobenthos communities (species composition, abundance and biomass) on the seafloor. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats”, “SD2– Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptor D5, Criterion D5C8, Descriptor D2, Criteria D2C1, D2C2 and D2C3, Descriptor D4, Criterion D4C2 and Descriptor D6, Criterion D6C5. 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 division) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency once 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. The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). 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: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass.	The aim of the programme is to monitor macrozoobenthos communities (species composition, abundance and biomass) on the seafloor. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats”, “SD2– Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptor D5, Criterion D5C8, Descriptor D2, Criteria D2C1, D2C2 and D2C3, Descriptor D4, Criterion D4C2 and Descriptor D6, Criterion D6C5. 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 division) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency once 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. The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). 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: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass.	The aim of the programme is to monitor macrozoobenthos communities (species composition, abundance and biomass) on the seafloor. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats”, “SD2– Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptor D5, Criterion D5C8, Descriptor D2, Criteria D2C1, D2C2 and D2C3, Descriptor D4, Criterion D4C2 and Descriptor D6, Criterion D6C5. 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 division) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency once 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. The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). 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: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass.	The aim of the programme is to monitor macrozoobenthos communities (species composition, abundance and biomass) on the seafloor. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats”, “SD2– Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptor D5, Criterion D5C8, Descriptor D2, Criteria D2C1, D2C2 and D2C3, Descriptor D4, Criterion D4C2 and Descriptor D6, Criterion D6C5. 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 division) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency once 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. The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). 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: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass.	The aim of the programme is to monitor macrozoobenthos communities (species composition, abundance and biomass) on the seafloor. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats”, “SD2– Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptor D5, Criterion D5C8, Descriptor D2, Criteria D2C1, D2C2 and D2C3, Descriptor D4, Criterion D4C2 and Descriptor D6, Criterion D6C5. 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 division) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency once 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. The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). 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: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass.	The aim of the programme is to collect data on the physical and chemical characteristics of the seabed, such as bathymetry, seabed substrate and morphology, as well as organic matter content in the sediments. Hydrographic surveying is the task of the Hydrographic service and data are made available via Maritime Administration. The seabed mapping process is continuous and the whole sea area is planned to be covered by 2030. Data on the seabed substrate and morphology is collected by project-based activities, and the distributions of seabed substrate and morphology in the Estonian waters are available at the Geological Survey and Land Board as well via the EMODnet Geology portal. Organic matter content is monitored at the macrozoobenthos stations and transects in the frames of the national environmental monitoring programme open sea monitoring programme. Data on organic matter are reported every year by 1 March and are made available via environmental database KESE. Monitoring is not HELCOM regionally coordinated, partly coordinated in collaboration with EMODnet Geology. The programme corresponds to the following monitoring programmes in the indicative list: Seabed habitats – physical and chemical characteristics.	The aim of the programme is to collect data on the physical and chemical characteristics of the seabed, such as bathymetry, seabed substrate and morphology, as well as organic matter content in the sediments. Hydrographic surveying is the task of the Hydrographic service and data are made available via Maritime Administration. The seabed mapping process is continuous and the whole sea area is planned to be covered by 2030. Data on the seabed substrate and morphology is collected by project-based activities, and the distributions of seabed substrate and morphology in the Estonian waters are available at the Geological Survey and Land Board as well via the EMODnet Geology portal. Organic matter content is monitored at the macrozoobenthos stations and transects in the frames of the national environmental monitoring programme open sea monitoring programme. Data on organic matter are reported every year by 1 March and are made available via environmental database KESE. Monitoring is not HELCOM regionally coordinated, partly coordinated in collaboration with EMODnet Geology. The programme corresponds to the following monitoring programmes in the indicative list: Seabed habitats – physical and chemical characteristics.	The aim of the programme is to collect data on the physical and chemical characteristics of the seabed, such as bathymetry, seabed substrate and morphology, as well as organic matter content in the sediments. Hydrographic surveying is the task of the Hydrographic service and data are made available via Maritime Administration. The seabed mapping process is continuous and the whole sea area is planned to be covered by 2030. Data on the seabed substrate and morphology is collected by project-based activities, and the distributions of seabed substrate and morphology in the Estonian waters are available at the Geological Survey and Land Board as well via the EMODnet Geology portal. Organic matter content is monitored at the macrozoobenthos stations and transects in the frames of the national environmental monitoring programme open sea monitoring programme. Data on organic matter are reported every year by 1 March and are made available via environmental database KESE. Monitoring is not HELCOM regionally coordinated, partly coordinated in collaboration with EMODnet Geology. The programme corresponds to the following monitoring programmes in the indicative list: Seabed habitats – physical and chemical characteristics.	The aim of the programme is to collect data on the physical and chemical characteristics of the seabed, such as bathymetry, seabed substrate and morphology, as well as organic matter content in the sediments. Hydrographic surveying is the task of the Hydrographic service and data are made available via Maritime Administration. The seabed mapping process is continuous and the whole sea area is planned to be covered by 2030. Data on the seabed substrate and morphology is collected by project-based activities, and the distributions of seabed substrate and morphology in the Estonian waters are available at the Geological Survey and Land Board as well via the EMODnet Geology portal. Organic matter content is monitored at the macrozoobenthos stations and transects in the frames of the national environmental monitoring programme open sea monitoring programme. Data on organic matter are reported every year by 1 March and are made available via environmental database KESE. Monitoring is not HELCOM regionally coordinated, partly coordinated in collaboration with EMODnet Geology. The programme corresponds to the following monitoring programmes in the indicative list: Seabed habitats – physical and chemical characteristics.	The aim of the programme is to assess physical loss and disturbance of seabed caused by human activities. It provides data to monitoring strategies „ SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats“ and “SD7 – Changes in hydrographic conditions”. The programme is related to GES Descriptor D6, Criteria D6C1, D6C2, D6C3 and D6C4; Descriptor D7, Criteria D7C1 and D7C2. Data are gathered through permitting database KOTKAS as well as project-based research. The program data collection is regionally coordinated (data delivered separately by each country) via HELCOM. There have been some updates, changes in programme structure and indicator developments since 2014. The programme corresponds to the following monitoring programmes in the indicative list: Physical loss - distribution and extent (from e.g. infrastructure, coastal protection); Physical disturbance - from dredging and disposal of dredged material; Physical disturbance - from sand and gravel extraction.	The aim of the programme is to assess physical loss and disturbance of seabed caused by human activities. It provides data to monitoring strategies „ SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats“ and “SD7 – Changes in hydrographic conditions”. The programme is related to GES Descriptor D6, Criteria D6C1, D6C2, D6C3 and D6C4; Descriptor D7, Criteria D7C1 and D7C2. Data are gathered through permitting database KOTKAS as well as project-based research. The program data collection is regionally coordinated (data delivered separately by each country) via HELCOM. There have been some updates, changes in programme structure and indicator developments since 2014. The programme corresponds to the following monitoring programmes in the indicative list: Physical loss - distribution and extent (from e.g. infrastructure, coastal protection); Physical disturbance - from dredging and disposal of dredged material; Physical disturbance - from sand and gravel extraction.	The aim of the programme is to assess physical loss and disturbance of seabed caused by human activities. It provides data to monitoring strategies „ SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats“ and “SD7 – Changes in hydrographic conditions”. The programme is related to GES Descriptor D6, Criteria D6C1, D6C2, D6C3 and D6C4; Descriptor D7, Criteria D7C1 and D7C2. Data are gathered through permitting database KOTKAS as well as project-based research. The program data collection is regionally coordinated (data delivered separately by each country) via HELCOM. There have been some updates, changes in programme structure and indicator developments since 2014. The programme corresponds to the following monitoring programmes in the indicative list: Physical loss - distribution and extent (from e.g. infrastructure, coastal protection); Physical disturbance - from dredging and disposal of dredged material; Physical disturbance - from sand and gravel extraction.	The aim of the programme is to assess physical loss and disturbance of seabed caused by human activities. It provides data to monitoring strategies „ SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats“ and “SD7 – Changes in hydrographic conditions”. The programme is related to GES Descriptor D6, Criteria D6C1, D6C2, D6C3 and D6C4; Descriptor D7, Criteria D7C1 and D7C2. Data are gathered through permitting database KOTKAS as well as project-based research. The program data collection is regionally coordinated (data delivered separately by each country) via HELCOM. There have been some updates, changes in programme structure and indicator developments since 2014. The programme corresponds to the following monitoring programmes in the indicative list: Physical loss - distribution and extent (from e.g. infrastructure, coastal protection); Physical disturbance - from dredging and disposal of dredged material; Physical disturbance - from sand and gravel extraction.	The aim of the programme is to assess physical loss and disturbance of seabed caused by human activities. It provides data to monitoring strategies „ SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats“ and “SD7 – Changes in hydrographic conditions”. The programme is related to GES Descriptor D6, Criteria D6C1, D6C2, D6C3 and D6C4; Descriptor D7, Criteria D7C1 and D7C2. Data are gathered through permitting database KOTKAS as well as project-based research. The program data collection is regionally coordinated (data delivered separately by each country) via HELCOM. There have been some updates, changes in programme structure and indicator developments since 2014. The programme corresponds to the following monitoring programmes in the indicative list: Physical loss - distribution and extent (from e.g. infrastructure, coastal protection); Physical disturbance - from dredging and disposal of dredged material; Physical disturbance - from sand and gravel extraction.	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 collect data on coastal morphology and dynamics (including erosion processes). It assesses changes of coasts (incl erosion, etc.) due to natural processes (storms, wave activity) and human-induced pressures. The coastal profile on-shore and in near-shore water, as well as the characteristics of the substrate, are recorded. Data on the substrate and morphology are collected yearly at the selected monitoring sites along the Estonian coasts by the Geological Survey. Data are reported every year by 1 March and are made available via national environmental database KESE.	The aim of the programme is to collect data on coastal morphology and dynamics (including erosion processes). It assesses changes of coasts (incl erosion, etc.) due to natural processes (storms, wave activity) and human-induced pressures. The coastal profile on-shore and in near-shore water, as well as the characteristics of the substrate, are recorded. Data on the substrate and morphology are collected yearly at the selected monitoring sites along the Estonian coasts by the Geological Survey. Data are reported every year by 1 March and are made available via national environmental database KESE.	The aim of the programme is to collect data on coastal morphology and dynamics (including erosion processes). It assesses changes of coasts (incl erosion, etc.) due to natural processes (storms, wave activity) and human-induced pressures. The coastal profile on-shore and in near-shore water, as well as the characteristics of the substrate, are recorded. Data on the substrate and morphology are collected yearly at the selected monitoring sites along the Estonian coasts by the Geological Survey. Data are reported every year by 1 March and are made available via national environmental database KESE.	The aim of the programme is to collect data on coastal morphology and dynamics (including erosion processes). It assesses changes of coasts (incl erosion, etc.) due to natural processes (storms, wave activity) and human-induced pressures. The coastal profile on-shore and in near-shore water, as well as the characteristics of the substrate, are recorded. Data on the substrate and morphology are collected yearly at the selected monitoring sites along the Estonian coasts by the Geological Survey. Data are reported every year by 1 March and are made available via national environmental database KESE.
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	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 Human activities causing the pressures Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures 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 Human activities causing the pressures Pressures in the marine environment	Environmental state and impacts Human activities causing the pressures Pressures in the marine environment	Environmental state and impacts Human activities causing the pressures Pressures in the marine environment	Environmental state and impacts Human activities causing the pressures 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	Habitats Directive Water Framework Directive	Habitats Directive Water Framework Directive	Habitats Directive Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats Directive Monitoring programme targeting at national legislation Water Framework Directive	Habitats 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	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 Water Framework Directive	Habitats Directive Maritime Spatial Planning Directive Water Framework Directive	Habitats Directive Maritime Spatial Planning Directive Water Framework Directive	Habitats Directive Maritime Spatial Planning Directive Water Framework 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	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM Other	HELCOM Other	HELCOM Other	HELCOM Other	HELCOM Other	HELCOM 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	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection
Monitoring details																								Seabed habitats monitoring combines different monitoring methodologies of monitoring of phyto- and zoobenthos. The monitoring for assessment of the Habitat Directive habitat types includes both, visual observations within ecological belts and in-situ sampling in representative sites. The total coverage, species abundance and coverage are registered as well as bottom sediment type. Biomass samples are collected by divers or grab samplers (soft bottom). Within the monitoring of commercial stock of Furcellaria lumbricalis, the thickness of algae layer, Secchi depth, temperature and dissolved oxygen in the near-bottom layer are also measured. The methodology for monitoring and assessment of habitat types 1130, 1150 and 1160 is still under development. Monitoring of seabed habitats of coastal water bodies includes determination of the presence and abundance of all species, coverage, sediment type and distribution depth limit within a transect. The observations are carried out at different transect depths up to macrophyte depth limit both by visual observation or using underwater video remote observation method once a year (from July to August). Quantitative samples are collected with the 20x20 metal frame and deep-freezed for laboratory analysis (excluding Furcellaria lumbricalis stock samples). In the laboratory, the species composition and species wet weight (red algae stock) or dry weight (seabed habitats and habitat types) per 1m2 are determined. The monitoring and data collection is partly coordinated by HELCOM and for softbottom habitats only.	Seabed habitats monitoring combines different monitoring methodologies of monitoring of phyto- and zoobenthos. The monitoring for assessment of the Habitat Directive habitat types includes both, visual observations within ecological belts and in-situ sampling in representative sites. The total coverage, species abundance and coverage are registered as well as bottom sediment type. Biomass samples are collected by divers or grab samplers (soft bottom). Within the monitoring of commercial stock of Furcellaria lumbricalis, the thickness of algae layer, Secchi depth, temperature and dissolved oxygen in the near-bottom layer are also measured. The methodology for monitoring and assessment of habitat types 1130, 1150 and 1160 is still under development. Monitoring of seabed habitats of coastal water bodies includes determination of the presence and abundance of all species, coverage, sediment type and distribution depth limit within a transect. The observations are carried out at different transect depths up to macrophyte depth limit both by visual observation or using underwater video remote observation method once a year (from July to August). Quantitative samples are collected with the 20x20 metal frame and deep-freezed for laboratory analysis (excluding Furcellaria lumbricalis stock samples). In the laboratory, the species composition and species wet weight (red algae stock) or dry weight (seabed habitats and habitat types) per 1m2 are determined. The monitoring and data collection is partly coordinated by HELCOM and for softbottom habitats only.	Seabed habitats monitoring combines different monitoring methodologies of monitoring of phyto- and zoobenthos. The monitoring for assessment of the Habitat Directive habitat types includes both, visual observations within ecological belts and in-situ sampling in representative sites. The total coverage, species abundance and coverage are registered as well as bottom sediment type. Biomass samples are collected by divers or grab samplers (soft bottom). Within the monitoring of commercial stock of Furcellaria lumbricalis, the thickness of algae layer, Secchi depth, temperature and dissolved oxygen in the near-bottom layer are also measured. The methodology for monitoring and assessment of habitat types 1130, 1150 and 1160 is still under development. Monitoring of seabed habitats of coastal water bodies includes determination of the presence and abundance of all species, coverage, sediment type and distribution depth limit within a transect. The observations are carried out at different transect depths up to macrophyte depth limit both by visual observation or using underwater video remote observation method once a year (from July to August). Quantitative samples are collected with the 20x20 metal frame and deep-freezed for laboratory analysis (excluding Furcellaria lumbricalis stock samples). In the laboratory, the species composition and species wet weight (red algae stock) or dry weight (seabed habitats and habitat types) per 1m2 are determined. The monitoring and data collection is partly coordinated by HELCOM and for softbottom habitats only.	The presence of species, total coverage and maximum distribution depth are registered during visual observations or using underwater video remote observation method. In the monitoring site, the total coverage of phytobenthos, species presence and their coverage, as well as sediment type are observed. Quantitative samples are collected by a diver with the 20x20 metal frame (in triplicate) and deep-freezed for laboratory analysis. In the laboratory, the species composition and dry weight of each species per 1m2 are determined. In frames of coastal waters monitoring, the total nitrogen, total phosphorus (6x per year) and PAR and water temperature are also registered (continuous measurements during 3-month period) in each monitoring area as supplementary information.	The presence of species, total coverage and maximum distribution depth are registered during visual observations or using underwater video remote observation method. In the monitoring site, the total coverage of phytobenthos, species presence and their coverage, as well as sediment type are observed. Quantitative samples are collected by a diver with the 20x20 metal frame (in triplicate) and deep-freezed for laboratory analysis. In the laboratory, the species composition and dry weight of each species per 1m2 are determined. In frames of coastal waters monitoring, the total nitrogen, total phosphorus (6x per year) and PAR and water temperature are also registered (continuous measurements during 3-month period) in each monitoring area as supplementary information.	The presence of species, total coverage and maximum distribution depth are registered during visual observations or using underwater video remote observation method. In the monitoring site, the total coverage of phytobenthos, species presence and their coverage, as well as sediment type are observed. Quantitative samples are collected by a diver with the 20x20 metal frame (in triplicate) and deep-freezed for laboratory analysis. In the laboratory, the species composition and dry weight of each species per 1m2 are determined. In frames of coastal waters monitoring, the total nitrogen, total phosphorus (6x per year) and PAR and water temperature are also registered (continuous measurements during 3-month period) in each monitoring area as supplementary information.	The presence of species, total coverage and maximum distribution depth are registered during visual observations or using underwater video remote observation method. In the monitoring site, the total coverage of phytobenthos, species presence and their coverage, as well as sediment type are observed. Quantitative samples are collected by a diver with the 20x20 metal frame (in triplicate) and deep-freezed for laboratory analysis. In the laboratory, the species composition and dry weight of each species per 1m2 are determined. In frames of coastal waters monitoring, the total nitrogen, total phosphorus (6x per year) and PAR and water temperature are also registered (continuous measurements during 3-month period) in each monitoring area as supplementary information.	The presence of species, total coverage and maximum distribution depth are registered during visual observations or using underwater video remote observation method. In the monitoring site, the total coverage of phytobenthos, species presence and their coverage, as well as sediment type are observed. Quantitative samples are collected by a diver with the 20x20 metal frame (in triplicate) and deep-freezed for laboratory analysis. In the laboratory, the species composition and dry weight of each species per 1m2 are determined. In frames of coastal waters monitoring, the total nitrogen, total phosphorus (6x per year) and PAR and water temperature are also registered (continuous measurements during 3-month period) in each monitoring area as supplementary information.	The presence of species, total coverage and maximum distribution depth are registered during visual observations or using underwater video remote observation method. In the monitoring site, the total coverage of phytobenthos, species presence and their coverage, as well as sediment type are observed. Quantitative samples are collected by a diver with the 20x20 metal frame (in triplicate) and deep-freezed for laboratory analysis. In the laboratory, the species composition and dry weight of each species per 1m2 are determined. In frames of coastal waters monitoring, the total nitrogen, total phosphorus (6x per year) and PAR and water temperature are also registered (continuous measurements during 3-month period) in each monitoring area as supplementary information.	Macrozoobenthos samples are collected once a year in off-shore areas and designated coastal waters and in rotation at least once in a 6-year period from other coastal waters. Van Veen or Ekman type grab samplers are used for sampling. The sediment type, concentration of dissolved oxygen in the near-bottom layer, concentration of H2S, water temperature and salinity are registered as supplementary information at the sampling site. Every sample is collected in triplicate and frozen for laboratory analyse. In the laboratory, the species composition, abundance of species and dry weight of every species (per 1 m2) is determined. For observation of maximum depth distribution of Limecola balthica, three designated transects are monitored in the open-sea area; samples (one sample per each depth point) are taken in accordance with the transect depth gradient.	Macrozoobenthos samples are collected once a year in off-shore areas and designated coastal waters and in rotation at least once in a 6-year period from other coastal waters. Van Veen or Ekman type grab samplers are used for sampling. The sediment type, concentration of dissolved oxygen in the near-bottom layer, concentration of H2S, water temperature and salinity are registered as supplementary information at the sampling site. Every sample is collected in triplicate and frozen for laboratory analyse. In the laboratory, the species composition, abundance of species and dry weight of every species (per 1 m2) is determined. For observation of maximum depth distribution of Limecola balthica, three designated transects are monitored in the open-sea area; samples (one sample per each depth point) are taken in accordance with the transect depth gradient.	Macrozoobenthos samples are collected once a year in off-shore areas and designated coastal waters and in rotation at least once in a 6-year period from other coastal waters. Van Veen or Ekman type grab samplers are used for sampling. The sediment type, concentration of dissolved oxygen in the near-bottom layer, concentration of H2S, water temperature and salinity are registered as supplementary information at the sampling site. Every sample is collected in triplicate and frozen for laboratory analyse. In the laboratory, the species composition, abundance of species and dry weight of every species (per 1 m2) is determined. For observation of maximum depth distribution of Limecola balthica, three designated transects are monitored in the open-sea area; samples (one sample per each depth point) are taken in accordance with the transect depth gradient.	Macrozoobenthos samples are collected once a year in off-shore areas and designated coastal waters and in rotation at least once in a 6-year period from other coastal waters. Van Veen or Ekman type grab samplers are used for sampling. The sediment type, concentration of dissolved oxygen in the near-bottom layer, concentration of H2S, water temperature and salinity are registered as supplementary information at the sampling site. Every sample is collected in triplicate and frozen for laboratory analyse. In the laboratory, the species composition, abundance of species and dry weight of every species (per 1 m2) is determined. For observation of maximum depth distribution of Limecola balthica, three designated transects are monitored in the open-sea area; samples (one sample per each depth point) are taken in accordance with the transect depth gradient.	Macrozoobenthos samples are collected once a year in off-shore areas and designated coastal waters and in rotation at least once in a 6-year period from other coastal waters. Van Veen or Ekman type grab samplers are used for sampling. The sediment type, concentration of dissolved oxygen in the near-bottom layer, concentration of H2S, water temperature and salinity are registered as supplementary information at the sampling site. Every sample is collected in triplicate and frozen for laboratory analyse. In the laboratory, the species composition, abundance of species and dry weight of every species (per 1 m2) is determined. For observation of maximum depth distribution of Limecola balthica, three designated transects are monitored in the open-sea area; samples (one sample per each depth point) are taken in accordance with the transect depth gradient.	Macrozoobenthos samples are collected once a year in off-shore areas and designated coastal waters and in rotation at least once in a 6-year period from other coastal waters. Van Veen or Ekman type grab samplers are used for sampling. The sediment type, concentration of dissolved oxygen in the near-bottom layer, concentration of H2S, water temperature and salinity are registered as supplementary information at the sampling site. Every sample is collected in triplicate and frozen for laboratory analyse. In the laboratory, the species composition, abundance of species and dry weight of every species (per 1 m2) is determined. For observation of maximum depth distribution of Limecola balthica, three designated transects are monitored in the open-sea area; samples (one sample per each depth point) are taken in accordance with the transect depth gradient.	Macrozoobenthos samples are collected once a year in off-shore areas and designated coastal waters and in rotation at least once in a 6-year period from other coastal waters. Van Veen or Ekman type grab samplers are used for sampling. The sediment type, concentration of dissolved oxygen in the near-bottom layer, concentration of H2S, water temperature and salinity are registered as supplementary information at the sampling site. Every sample is collected in triplicate and frozen for laboratory analyse. In the laboratory, the species composition, abundance of species and dry weight of every species (per 1 m2) is determined. For observation of maximum depth distribution of Limecola balthica, three designated transects are monitored in the open-sea area; samples (one sample per each depth point) are taken in accordance with the transect depth gradient.	Macrozoobenthos samples are collected once a year in off-shore areas and designated coastal waters and in rotation at least once in a 6-year period from other coastal waters. Van Veen or Ekman type grab samplers are used for sampling. The sediment type, concentration of dissolved oxygen in the near-bottom layer, concentration of H2S, water temperature and salinity are registered as supplementary information at the sampling site. Every sample is collected in triplicate and frozen for laboratory analyse. In the laboratory, the species composition, abundance of species and dry weight of every species (per 1 m2) is determined. For observation of maximum depth distribution of Limecola balthica, three designated transects are monitored in the open-sea area; samples (one sample per each depth point) are taken in accordance with the transect depth gradient.	Macrozoobenthos samples are collected once a year in off-shore areas and designated coastal waters and in rotation at least once in a 6-year period from other coastal waters. Van Veen or Ekman type grab samplers are used for sampling. The sediment type, concentration of dissolved oxygen in the near-bottom layer, concentration of H2S, water temperature and salinity are registered as supplementary information at the sampling site. Every sample is collected in triplicate and frozen for laboratory analyse. In the laboratory, the species composition, abundance of species and dry weight of every species (per 1 m2) is determined. For observation of maximum depth distribution of Limecola balthica, three designated transects are monitored in the open-sea area; samples (one sample per each depth point) are taken in accordance with the transect depth gradient.	Monitoring is performed by the Maritime Administration and the Geological Survey of Estonia as fulfilment of state obligations and project-based activities. The organic matter content of bottom sediments is determined within the national environmental monitoring programme. Bathymetry surveys are performed with sonar. The seabed mapping is done using geophysical equipment – a seismic-acoustic profiler (operating frequency 0-450 Hz), a low-frequency acoustic profiler (24 kHz), an echo-sounder, side-scan sonar and probe tools. For determination of the organic matter content in sediment samples, loss on ignition method is used. The bathymetric measurements are being performed continually unless the entire Estonian marine area is covered. The data on the seabed substrate and morphology is also collected by project-based activities. Organic matter sampling is performed annually once a year.	Monitoring is performed by the Maritime Administration and the Geological Survey of Estonia as fulfilment of state obligations and project-based activities. The organic matter content of bottom sediments is determined within the national environmental monitoring programme. Bathymetry surveys are performed with sonar. The seabed mapping is done using geophysical equipment – a seismic-acoustic profiler (operating frequency 0-450 Hz), a low-frequency acoustic profiler (24 kHz), an echo-sounder, side-scan sonar and probe tools. For determination of the organic matter content in sediment samples, loss on ignition method is used. The bathymetric measurements are being performed continually unless the entire Estonian marine area is covered. The data on the seabed substrate and morphology is also collected by project-based activities. Organic matter sampling is performed annually once a year.	Monitoring is performed by the Maritime Administration and the Geological Survey of Estonia as fulfilment of state obligations and project-based activities. The organic matter content of bottom sediments is determined within the national environmental monitoring programme. Bathymetry surveys are performed with sonar. The seabed mapping is done using geophysical equipment – a seismic-acoustic profiler (operating frequency 0-450 Hz), a low-frequency acoustic profiler (24 kHz), an echo-sounder, side-scan sonar and probe tools. For determination of the organic matter content in sediment samples, loss on ignition method is used. The bathymetric measurements are being performed continually unless the entire Estonian marine area is covered. The data on the seabed substrate and morphology is also collected by project-based activities. Organic matter sampling is performed annually once a year.	Monitoring is performed by the Maritime Administration and the Geological Survey of Estonia as fulfilment of state obligations and project-based activities. The organic matter content of bottom sediments is determined within the national environmental monitoring programme. Bathymetry surveys are performed with sonar. The seabed mapping is done using geophysical equipment – a seismic-acoustic profiler (operating frequency 0-450 Hz), a low-frequency acoustic profiler (24 kHz), an echo-sounder, side-scan sonar and probe tools. For determination of the organic matter content in sediment samples, loss on ignition method is used. The bathymetric measurements are being performed continually unless the entire Estonian marine area is covered. The data on the seabed substrate and morphology is also collected by project-based activities. Organic matter sampling is performed annually once a year.	The extent of adverse effects from anthropogenic pressures on the seabed is determined using the information on the following human activities: dredging, dumping, bottom trawling, mining, construction of facilities at sea, etc. A proportion (percentage) of the total extent of the habitat type directly affected by human activities is assessed using overlay analysis performed in the geographical information system. The precondition for the analysis is the existence of georeferenced spatial data layers with updated information on human activities (dredging, dumping, bottom trawling, etc). The extent of hydrographical changes is assessed with mathematical modelling. For dredging and dumping works monitoring, in addition to volume and area measurements suspended matter and turbidity are measured in-situ (standard EVS-EN 872). The monitoring frequency is irregular and/or as regulated by environmental permits. The data are both raw data and based on it spatial (processed) data with no common place yet, where it could be accessed.	The extent of adverse effects from anthropogenic pressures on the seabed is determined using the information on the following human activities: dredging, dumping, bottom trawling, mining, construction of facilities at sea, etc. A proportion (percentage) of the total extent of the habitat type directly affected by human activities is assessed using overlay analysis performed in the geographical information system. The precondition for the analysis is the existence of georeferenced spatial data layers with updated information on human activities (dredging, dumping, bottom trawling, etc). The extent of hydrographical changes is assessed with mathematical modelling. For dredging and dumping works monitoring, in addition to volume and area measurements suspended matter and turbidity are measured in-situ (standard EVS-EN 872). The monitoring frequency is irregular and/or as regulated by environmental permits. The data are both raw data and based on it spatial (processed) data with no common place yet, where it could be accessed.	The extent of adverse effects from anthropogenic pressures on the seabed is determined using the information on the following human activities: dredging, dumping, bottom trawling, mining, construction of facilities at sea, etc. A proportion (percentage) of the total extent of the habitat type directly affected by human activities is assessed using overlay analysis performed in the geographical information system. The precondition for the analysis is the existence of georeferenced spatial data layers with updated information on human activities (dredging, dumping, bottom trawling, etc). The extent of hydrographical changes is assessed with mathematical modelling. For dredging and dumping works monitoring, in addition to volume and area measurements suspended matter and turbidity are measured in-situ (standard EVS-EN 872). The monitoring frequency is irregular and/or as regulated by environmental permits. The data are both raw data and based on it spatial (processed) data with no common place yet, where it could be accessed.	The extent of adverse effects from anthropogenic pressures on the seabed is determined using the information on the following human activities: dredging, dumping, bottom trawling, mining, construction of facilities at sea, etc. A proportion (percentage) of the total extent of the habitat type directly affected by human activities is assessed using overlay analysis performed in the geographical information system. The precondition for the analysis is the existence of georeferenced spatial data layers with updated information on human activities (dredging, dumping, bottom trawling, etc). The extent of hydrographical changes is assessed with mathematical modelling. For dredging and dumping works monitoring, in addition to volume and area measurements suspended matter and turbidity are measured in-situ (standard EVS-EN 872). The monitoring frequency is irregular and/or as regulated by environmental permits. The data are both raw data and based on it spatial (processed) data with no common place yet, where it could be accessed.	The extent of adverse effects from anthropogenic pressures on the seabed is determined using the information on the following human activities: dredging, dumping, bottom trawling, mining, construction of facilities at sea, etc. A proportion (percentage) of the total extent of the habitat type directly affected by human activities is assessed using overlay analysis performed in the geographical information system. The precondition for the analysis is the existence of georeferenced spatial data layers with updated information on human activities (dredging, dumping, bottom trawling, etc). The extent of hydrographical changes is assessed with mathematical modelling. For dredging and dumping works monitoring, in addition to volume and area measurements suspended matter and turbidity are measured in-situ (standard EVS-EN 872). The monitoring frequency is irregular and/or as regulated by environmental permits. The data are both raw data and based on it spatial (processed) data with no common place yet, where it could be accessed.	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).	On-shore and near-shore measurements of coastal slope are conducted during the monitoring. For slope surveys geophysical equipment – profilers, echo-sounder and side-scan sonar are used. The sediment type, composition and its distribution and seabed morphology are recorded. The monitoring is carried out yearly with rotation at designated sites so that each site is monitored at least once in the 6-year period. Additionally, remote sensing (satellite images, orthophotos) are used to assess the changes in coastal areas.	On-shore and near-shore measurements of coastal slope are conducted during the monitoring. For slope surveys geophysical equipment – profilers, echo-sounder and side-scan sonar are used. The sediment type, composition and its distribution and seabed morphology are recorded. The monitoring is carried out yearly with rotation at designated sites so that each site is monitored at least once in the 6-year period. Additionally, remote sensing (satellite images, orthophotos) are used to assess the changes in coastal areas.	On-shore and near-shore measurements of coastal slope are conducted during the monitoring. For slope surveys geophysical equipment – profilers, echo-sounder and side-scan sonar are used. The sediment type, composition and its distribution and seabed morphology are recorded. The monitoring is carried out yearly with rotation at designated sites so that each site is monitored at least once in the 6-year period. Additionally, remote sensing (satellite images, orthophotos) are used to assess the changes in coastal areas.	On-shore and near-shore measurements of coastal slope are conducted during the monitoring. For slope surveys geophysical equipment – profilers, echo-sounder and side-scan sonar are used. The sediment type, composition and its distribution and seabed morphology are recorded. The monitoring is carried out yearly with rotation at designated sites so that each site is monitored at least once in the 6-year period. Additionally, remote sensing (satellite images, orthophotos) are used to assess the changes in coastal areas.
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)	Litter in the environment	Benthic broad habitats	Benthic broad habitats	Litter in the environment	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Eutrophication	Eutrophication	Benthic broad habitats	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Coastal ecosystems	Coastal ecosystems	Coastal ecosystems	Eutrophication	Benthic broad habitats	Benthic broad habitats	Physical loss of the seabed	Benthic broad habitats	Hydrographical changes	Hydrographical changes	Physical loss of the seabed	Physical disturbance to seabed	Benthic broad habitats	Benthic broad habitats	Benthic broad habitats	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	Hydrographical changes	Hydrographical changes	Physical and hydrological characteristics	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	Macrolitter (all)	Benthic habitats	Circalittoral coarse sediment Circalittoral mixed sediment Circalittoral mud Circalittoral rock and biogenic reef Circalittoral sand Infralittoral coarse sediment Infralittoral mixed sediment Infralittoral mud Infralittoral rock and biogenic reef Infralittoral sand	Macrolitter (all)	Not Applicable	Not Applicable	Benthic habitats - opportunistic macroalgae	Benthic habitats - macrophyte communities	Benthic habitats Circalittoral coarse sediment Circalittoral mixed sediment Circalittoral mud Circalittoral rock and biogenic reef Circalittoral sand Infralittoral coarse sediment Infralittoral mixed sediment Infralittoral mud Infralittoral rock and biogenic reef Infralittoral sand	Not Applicable	Not Applicable	Not Applicable	Deposit-feeders Sub-apex demersal predators	Deposit-feeders	Sub-apex demersal predators	Benthic habitats - macrobenthic communities	Benthic habitats Circalittoral coarse sediment Circalittoral mixed sediment Circalittoral mud Circalittoral rock and biogenic reef Circalittoral sand Infralittoral coarse sediment Infralittoral mixed sediment Infralittoral mud Infralittoral rock and biogenic reef Infralittoral sand	Benthic habitats Circalittoral coarse sediment Circalittoral mixed sediment Circalittoral mud Circalittoral rock and biogenic reef Circalittoral sand Infralittoral coarse sediment Infralittoral mixed sediment Infralittoral mud Infralittoral rock and biogenic reef Infralittoral sand	Not Applicable	Benthic habitats Circalittoral coarse sediment Circalittoral mixed sediment Circalittoral mud Circalittoral rock and biogenic reef Circalittoral sand Infralittoral coarse sediment Infralittoral mixed sediment Infralittoral mud Infralittoral rock and biogenic reef Infralittoral sand	Bathymetry	Seabed substrate and morphology	Not Applicable	Not Applicable	Benthic habitats Circalittoral coarse sediment Circalittoral mixed sediment Circalittoral mud Circalittoral rock and biogenic reef Circalittoral sand Infralittoral coarse sediment Infralittoral mixed sediment Infralittoral mud Infralittoral rock and biogenic reef Infralittoral sand	Benthic habitats Circalittoral coarse sediment Circalittoral mixed sediment Circalittoral mud Circalittoral rock and biogenic reef Circalittoral sand Infralittoral coarse sediment Infralittoral mixed sediment Infralittoral mud Infralittoral rock and biogenic reef Infralittoral sand	Circalittoral coarse sediment Circalittoral mixed sediment Circalittoral mud Circalittoral rock and biogenic reef Circalittoral sand Infralittoral coarse sediment Infralittoral mixed sediment Infralittoral mud Infralittoral rock and biogenic reef Infralittoral sand	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	Bathymetry	Seabed substrate and morphology	Bathymetry	Seabed substrate and morphology
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	D10C1	D6C5	D6C5	D10C1	D2C1	D2C2	D5C6	D5C7	D6C5	D2C1	D2C2	D2C3	D4C1	D4C2	D4C2	D5C8	D6C4	D6C5	D6C1	D6C5	D7C1	D7C1	D6C1	D6C2	D6C3	D6C4	D7C2	D5C1	D5C5	NotRelevan	D5C4	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	D7C1	D7C1	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	Amount on seabed	Extent Other	Other	Amount on seabed	Other Presence	Abundance (number of individuals) Biomass	Other	Other	Other	Other Presence	Abundance (number of individuals) Biomass	Other	Other	Abundance (number of individuals) Biomass Other	Abundance (number of individuals) Biomass	Abundance (number of individuals) Extent Other	Extent	Other	Other	Other	Other	Other	Extent	Extent Other	Extent	Extent	Other	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	Other	Bathymetric depth	Physical structure of habitat (e.g. sediment characteristics, topographic structure)
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; Presence; Biomass; Maximum de	Species composition; Presence; Biomass; Maximum de		Abundance (number of individuals); Biomass		Species composition; Presence; Relative abundance	Species composition; Presence; Relative abundance	Species composition; Presence; Relative abundance	Abundance (number of individuals); Biomass		Abundance (number of individuals); Biomass	Species composition	Extent	Extent	Species composition; Biomass		Species composition; Abundance; Biomass	Bathymetric depth; Physical structure of habitat (	Organic matter concentration in sediment (total)	Bathymetric depth	Physical structure of habitat (e.g. sediment chara		Turbidity			Extent											Direction	Water level	Significant wave height; Period; Direction	Direction	Water level	Significant wave height; Period; Direction	Bathymetric depth	Physical structure of habitat (e.g. sediment chara
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)	Coastal waters (WFD)	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	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)
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-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-NBP-EE-EEEE_10	BAL-EE-AA 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-NBP-EE-EEEE_10	BAL-EE-AA 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-NBP-EE-EEEE_10	BAL-EE-AA 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-NBP-EE-EEEE_10	BAL-EE-AA 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-NBP-EE-EEEE_10	BAL-EE-AA 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-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-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-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	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-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-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-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-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	1974-9999	1974-9999	1974-9999	1995-9999	1995-9999	1995-9999	1995-9999	1995-9999	1995-9999	1991-9999	1991-9999	1991-9999	1991-9999	1991-9999	1991-9999	1991-9999	1991-9999	1991-9999	1981-9999	1981-9999	1981-9999	1981-9999	1992-9999	1992-9999	1992-9999	1992-9999	1992-9999	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	1994-9999	1994-9999	1994-9999	1994-9999
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	Other	Other	Other	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Continually	Continually	Continually	Continually	Other	Other	Other	Other	Other	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Continually	Continually	Continually	Continually	Continually	Continually	Yearly	Yearly	Yearly	Yearly
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 Remote surveillance Visual observation	In-situ sampling coastal In-situ sampling offshore Remote surveillance Visual observation	In-situ sampling coastal In-situ sampling offshore Remote surveillance Visual observation	In-situ sampling coastal Remote surveillance Visual observation	In-situ sampling coastal Remote surveillance Visual observation	In-situ sampling coastal Remote surveillance Visual observation	In-situ sampling coastal Remote surveillance Visual observation	In-situ sampling coastal Remote surveillance Visual observation	In-situ sampling coastal Remote surveillance Visual observation	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 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 surveillance	In-situ sampling coastal In-situ sampling offshore Remote surveillance	In-situ sampling coastal In-situ sampling offshore Remote surveillance	In-situ sampling coastal In-situ sampling offshore Remote surveillance	Administrative data collection Ecological modelling In-situ sampling coastal In-situ sampling offshore Numerical modelling Other	Administrative data collection Ecological modelling In-situ sampling coastal In-situ sampling offshore Numerical modelling Other	Administrative data collection Ecological modelling In-situ sampling coastal In-situ sampling offshore Numerical modelling Other	Administrative data collection Ecological modelling In-situ sampling coastal In-situ sampling offshore Numerical modelling Other	Administrative data collection Ecological modelling In-situ sampling coastal In-situ sampling offshore Numerical modelling Other	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	In-situ sampling coastal Remote satellite imagery Remote surveillance	In-situ sampling coastal Remote satellite imagery Remote surveillance	In-situ sampling coastal Remote satellite imagery Remote surveillance	In-situ sampling coastal Remote satellite imagery Remote surveillance
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 Manual for monitoring in COMBINE programme Other monitoring method	HELCOM Manual for monitoring in COMBINE programme Other monitoring method	HELCOM Manual for monitoring in COMBINE programme Other monitoring method	HELCOM Manual for monitoring in COMBINE programme	HELCOM Manual for monitoring in COMBINE programme	HELCOM Manual for monitoring in COMBINE programme	HELCOM Manual for monitoring in COMBINE programme	HELCOM Manual for monitoring in COMBINE programme	HELCOM Manual for monitoring in COMBINE programme	OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) Other monitoring method	OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) Other monitoring method	OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) Other monitoring method	OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) Other monitoring method	OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) Other monitoring method	OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) Other monitoring method	OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) Other monitoring method	OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) Other monitoring method	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 measuring turbidity Other monitoring method	HELCOM Guidelines for measuring turbidity Other monitoring method	HELCOM Guidelines for measuring turbidity Other monitoring method	HELCOM Guidelines for measuring turbidity Other monitoring method	HELCOM Guidelines for measuring turbidity Other monitoring method	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	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.	National monitoring programme	National monitoring programme	National monitoring programme							National monitoring programme	National monitoring programme	National monitoring programme	National monitoring programme	National monitoring programme	National monitoring programme	National monitoring programme	National monitoring programme	National monitoring programme	The description of methodology and technique that is used for bathymetry surveys is available at http://adam.vta.ee/teenused/hnt/yldinfo/tehnika.html.	The description of methodology and technique that is used for bathymetry surveys is available at http://adam.vta.ee/teenused/hnt/yldinfo/tehnika.html.	The description of methodology and technique that is used for bathymetry surveys is available at http://adam.vta.ee/teenused/hnt/yldinfo/tehnika.html.	The description of methodology and technique that is used for bathymetry surveys is available at http://adam.vta.ee/teenused/hnt/yldinfo/tehnika.html.	The description of the method is available from https://www.envir.ee/sites/default/files/msrd_lavivaartused_lopparuanne.pdf	The description of the method is available from https://www.envir.ee/sites/default/files/msrd_lavivaartused_lopparuanne.pdf	The description of the method is available from https://www.envir.ee/sites/default/files/msrd_lavivaartused_lopparuanne.pdf	The description of the method is available from https://www.envir.ee/sites/default/files/msrd_lavivaartused_lopparuanne.pdf	The description of the method is available from https://www.envir.ee/sites/default/files/msrd_lavivaartused_lopparuanne.pdf											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/).	Nationally accredited methods, geodetical and geophysical surveys and measurements.	Nationally accredited methods, geodetical and geophysical surveys and measurements.	Nationally accredited methods, geodetical and geophysical surveys and measurements.	Nationally accredited methods, geodetical and geophysical surveys and measurements.
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.	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and HELCOM recommendations of monitoring manuals are followed (if applicable)	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and HELCOM recommendations of monitoring manuals are followed (if applicable)	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and HELCOM recommendations of monitoring manuals are followed (if applicable)	The quality is ensured by following the HELCOM guidances recommendations, 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 ensured by following the HELCOM guidances recommendations, 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 ensured by following the HELCOM guidances recommendations, 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 ensured by following the HELCOM guidances recommendations, 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 ensured by following the HELCOM guidances recommendations, 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 ensured by following the HELCOM guidances recommendations, 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 ensured by following the OSPAR/HELCOM guidance (OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) recommendations, 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 ensured by following the OSPAR/HELCOM guidance (OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) recommendations, 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 ensured by following the OSPAR/HELCOM guidance (OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) recommendations, 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 ensured by following the OSPAR/HELCOM guidance (OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) recommendations, 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 ensured by following the OSPAR/HELCOM guidance (OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) recommendations, 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 ensured by following the OSPAR/HELCOM guidance (OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) recommendations, 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 ensured by following the OSPAR/HELCOM guidance (OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) recommendations, 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 ensured by following the OSPAR/HELCOM guidance (OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) recommendations, 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 ensured by following the OSPAR/HELCOM guidance (OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) recommendations, 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 of bathymetry surveys is guaranteed by IHO standard S44: http://www.iho.int/iho_pubs/standard/S-44_5E.pdf. The quality of the data submitted by the Estonian Geological Survey is guaranteed by the respective licenses and accreditations.	The quality of bathymetry surveys is guaranteed by IHO standard S44: http://www.iho.int/iho_pubs/standard/S-44_5E.pdf. The quality of the data submitted by the Estonian Geological Survey is guaranteed by the respective licenses and accreditations.	The quality of bathymetry surveys is guaranteed by IHO standard S44: http://www.iho.int/iho_pubs/standard/S-44_5E.pdf. The quality of the data submitted by the Estonian Geological Survey is guaranteed by the respective licenses and accreditations.	The quality of bathymetry surveys is guaranteed by IHO standard S44: http://www.iho.int/iho_pubs/standard/S-44_5E.pdf. The quality of the data submitted by the Estonian Geological Survey is guaranteed by the respective licenses and accreditations.	The quality is ensured by following standards and accreditation of experts and persons by whom the monitoring is performed, by local validation of the models used is made and by controls of the fulfilment of environmental permits' requirements and related reports.	The quality is ensured by following standards and accreditation of experts and persons by whom the monitoring is performed, by local validation of the models used is made and by controls of the fulfilment of environmental permits' requirements and related reports.	The quality is ensured by following standards and accreditation of experts and persons by whom the monitoring is performed, by local validation of the models used is made and by controls of the fulfilment of environmental permits' requirements and related reports.	The quality is ensured by following standards and accreditation of experts and persons by whom the monitoring is performed, by local validation of the models used is made and by controls of the fulfilment of environmental permits' requirements and related reports.	The quality is ensured by following standards and accreditation of experts and persons by whom the monitoring is performed, by local validation of the models used is made and by controls of the fulfilment of environmental permits' requirements and related reports.	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.	Quality is assured by fulfilling quality requirements for laboratories (incl. accreditation), following surveying instructions, properly calibrated measuring instruments and QA / QC of databases.	Quality is assured by fulfilling quality requirements for laboratories (incl. accreditation), following surveying instructions, properly calibrated measuring instruments and QA / QC of databases.	Quality is assured by fulfilling quality requirements for laboratories (incl. accreditation), following surveying instructions, properly calibrated measuring instruments and QA / QC of databases.	Quality is assured by fulfilling quality requirements for laboratories (incl. accreditation), following surveying instructions, properly calibrated measuring instruments and QA / QC of databases.
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.	Gathered data are submitted to the national environmental monitoring database KESE.	Gathered data are submitted to the national environmental monitoring database KESE.	Gathered data are submitted to the national environmental monitoring database KESE.	Gathered data are reported to the national environmental monitoring database KESE.	Gathered data are reported to the national environmental monitoring database KESE.	Gathered data are reported to the national environmental monitoring database KESE.	Gathered data are reported to the national environmental monitoring database KESE.	Gathered data are reported to the national environmental monitoring database KESE.	Gathered data are reported to the national environmental monitoring database KESE.	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) 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).	The data of the distribution of seabed substrate and morphology in the Estonian waters are available at the Geological Survey and Land Board and uploaded to the EMODnet Geology portal. Data on organic matter are reported every year by 1 March and are made available via national environmental database KESE. Spatial data (processed data) is created and made available based on measurements of raw data.	The data of the distribution of seabed substrate and morphology in the Estonian waters are available at the Geological Survey and Land Board and uploaded to the EMODnet Geology portal. Data on organic matter are reported every year by 1 March and are made available via national environmental database KESE. Spatial data (processed data) is created and made available based on measurements of raw data.	The data of the distribution of seabed substrate and morphology in the Estonian waters are available at the Geological Survey and Land Board and uploaded to the EMODnet Geology portal. Data on organic matter are reported every year by 1 March and are made available via national environmental database KESE. Spatial data (processed data) is created and made available based on measurements of raw data.	The data of the distribution of seabed substrate and morphology in the Estonian waters are available at the Geological Survey and Land Board and uploaded to the EMODnet Geology portal. Data on organic matter are reported every year by 1 March and are made available via national environmental database KESE. Spatial data (processed data) is created and made available based on measurements of raw data.	The data is compiled and updated at least once in the 6-year period. The common place, where the data access could be provided is still under development.	The data is compiled and updated at least once in the 6-year period. The common place, where the data access could be provided is still under development.	The data is compiled and updated at least once in the 6-year period. The common place, where the data access could be provided is still under development.	The data is compiled and updated at least once in the 6-year period. The common place, where the data access could be provided is still under development.	The data is compiled and updated at least once in the 6-year period. The common place, where the data access could be provided is still under development.	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 processed data are yearly reported to the national environmental monitoring database KESE. The original raw data are stored at the Geological Survey. Orthophotos are stored in Land Board.	The processed data are yearly reported to the national environmental monitoring database KESE. The original raw data are stored at the Geological Survey. Orthophotos are stored in Land Board.	The processed data are yearly reported to the national environmental monitoring database KESE. The original raw data are stored at the Geological Survey. Orthophotos are stored in Land Board.	The processed data are yearly reported to the national environmental monitoring database KESE. The original raw data are stored at the Geological Survey. Orthophotos are stored in Land Board.
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	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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egevused/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	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	http://195.80.112.238:8080/HIS/Avalik?REQUEST=Main,http://www.emodnet-geology.eu/,https://geoportaal.maaamet.ee/est/Ruumiandmed/Geoloogilised-andmed-p115.html,https://kese.envir.ee	http://195.80.112.238:8080/HIS/Avalik?REQUEST=Main,http://www.emodnet-geology.eu/,https://geoportaal.maaamet.ee/est/Ruumiandmed/Geoloogilised-andmed-p115.html,https://kese.envir.ee	http://195.80.112.238:8080/HIS/Avalik?REQUEST=Main,http://www.emodnet-geology.eu/,https://geoportaal.maaamet.ee/est/Ruumiandmed/Geoloogilised-andmed-p115.html,https://kese.envir.ee	http://195.80.112.238:8080/HIS/Avalik?REQUEST=Main,http://www.emodnet-geology.eu/,https://geoportaal.maaamet.ee/est/Ruumiandmed/Geoloogilised-andmed-p115.html,https://kese.envir.ee	https://kotkas.envir.ee/	https://kotkas.envir.ee/	https://kotkas.envir.ee/	https://kotkas.envir.ee/	https://kotkas.envir.ee/	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee,https://www.emodnet-physics.eu/Portal	https://kese.envir.ee,https://www.emodnet-physics.eu/Portal	https://kese.envir.ee,https://www.emodnet-physics.eu/Portal	https://kese.envir.ee,https://www.emodnet-physics.eu/Portal	https://kese.envir.ee,https://www.emodnet-physics.eu/Portal	https://kese.envir.ee,https://www.emodnet-physics.eu/Portal	https://kese.envir.ee,https://www.emodnet-physics.eu/Portal	https://marine.copernicus.eu/,https://www.emodnet-physics.eu/Portal	https://marine.copernicus.eu/,https://www.emodnet-physics.eu/Portal	https://marine.copernicus.eu/,https://www.emodnet-physics.eu/Portal	https://marine.copernicus.eu/,https://www.emodnet-physics.eu/Portal	https://marine.copernicus.eu/,https://www.emodnet-physics.eu/Portal	https://marine.copernicus.eu/,https://www.emodnet-physics.eu/Portal	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee
Related indicator/name																								Quality of habitat type mudflats and sandflats (code 1140) Quality of habitat type reefs (code 1170) Quality of habitat type sandbanks (code 1110) Quality of habitat type estuaries (code 1130) Quality of habitat type large shallow inlets and bays (code 1160) BALEED6C5.10 BALEED6C5.11 BALEED6C5.12 BALEED6C5.13 BALEED6C5.14 BALEED6C5.15 BALEED6C5.16 BALEED6C5.18 BALEED6C5.6 BALEED6C5.7 BALEED6C5.8 BALEED6C5.9	Quality of habitat type mudflats and sandflats (code 1140) Quality of habitat type reefs (code 1170) Quality of habitat type sandbanks (code 1110) Quality of habitat type estuaries (code 1130) Quality of habitat type large shallow inlets and bays (code 1160) BALEED6C5.10 BALEED6C5.11 BALEED6C5.12 BALEED6C5.13 BALEED6C5.14 BALEED6C5.15 BALEED6C5.16 BALEED6C5.18 BALEED6C5.6 BALEED6C5.7 BALEED6C5.8 BALEED6C5.9	Quality of habitat type mudflats and sandflats (code 1140) Quality of habitat type reefs (code 1170) Quality of habitat type sandbanks (code 1110) Quality of habitat type estuaries (code 1130) Quality of habitat type large shallow inlets and bays (code 1160) BALEED6C5.10 BALEED6C5.11 BALEED6C5.12 BALEED6C5.13 BALEED6C5.14 BALEED6C5.15 BALEED6C5.16 BALEED6C5.18 BALEED6C5.6 BALEED6C5.7 BALEED6C5.8 BALEED6C5.9	Biomass of alien benthic invertebrate species Macrolitter on seafloor in coastal sea [natural areas] Number of new non-indigenous species Proportion of opportunistic species BALEED5C7.4	Biomass of alien benthic invertebrate species Macrolitter on seafloor in coastal sea [natural areas] Number of new non-indigenous species Proportion of opportunistic species BALEED5C7.4	Biomass of alien benthic invertebrate species Macrolitter on seafloor in coastal sea [natural areas] Number of new non-indigenous species Proportion of opportunistic species BALEED5C7.4	Biomass of alien benthic invertebrate species Macrolitter on seafloor in coastal sea [natural areas] Number of new non-indigenous species Proportion of opportunistic species BALEED5C7.4	Biomass of alien benthic invertebrate species Macrolitter on seafloor in coastal sea [natural areas] Number of new non-indigenous species Proportion of opportunistic species BALEED5C7.4	Biomass of alien benthic invertebrate species Macrolitter on seafloor in coastal sea [natural areas] Number of new non-indigenous species Proportion of opportunistic species BALEED5C7.4	Biomass of alien benthic invertebrate species Biopollution level (BPL) Contribution of non-indigenous species in macrozoobenthic community Number of new non-indigenous species Zoobenthos community index BALEED5C8.3	Biomass of alien benthic invertebrate species Biopollution level (BPL) Contribution of non-indigenous species in macrozoobenthic community Number of new non-indigenous species Zoobenthos community index BALEED5C8.3	Biomass of alien benthic invertebrate species Biopollution level (BPL) Contribution of non-indigenous species in macrozoobenthic community Number of new non-indigenous species Zoobenthos community index BALEED5C8.3	Biomass of alien benthic invertebrate species Biopollution level (BPL) Contribution of non-indigenous species in macrozoobenthic community Number of new non-indigenous species Zoobenthos community index BALEED5C8.3	Biomass of alien benthic invertebrate species Biopollution level (BPL) Contribution of non-indigenous species in macrozoobenthic community Number of new non-indigenous species Zoobenthos community index BALEED5C8.3	Biomass of alien benthic invertebrate species Biopollution level (BPL) Contribution of non-indigenous species in macrozoobenthic community Number of new non-indigenous species Zoobenthos community index BALEED5C8.3	Biomass of alien benthic invertebrate species Biopollution level (BPL) Contribution of non-indigenous species in macrozoobenthic community Number of new non-indigenous species Zoobenthos community index BALEED5C8.3	Biomass of alien benthic invertebrate species Biopollution level (BPL) Contribution of non-indigenous species in macrozoobenthic community Number of new non-indigenous species Zoobenthos community index BALEED5C8.3	Biomass of alien benthic invertebrate species Biopollution level (BPL) Contribution of non-indigenous species in macrozoobenthic community Number of new non-indigenous species Zoobenthos community index BALEED5C8.3	BALEED6C5.17	BALEED6C5.17	BALEED6C5.17	BALEED6C5.17	Spatial distibution and area of alterations of hydrographic conditions Spatial distibution and area of physical disturbance to the seabed. Spatial distibution and area of physical loss of the natural seabed The spatial area of hydrographically altered habitat type estuaries (code 1130) The spatial area of hydrographically altered habitat type large shallow inlets and bays (code 1160) The spatial area of hydrographically altered habitat type mudflats and sandflats (code 1140) The spatial area of hydrographically altered habitat type reefs (code 1170) The spatial area of hydrographically altered habitat type sandbanks (code 1110) The spatial area of loss of the habitat type estuaries (code 1130) resulting from anthropogenic loss of the natural seabed The spatial area of loss of the habitat type large shallow inlets and bays (code 1160) resulting from anthropogenic loss of the natural seabed The spatial area of loss of the habitat type mudflats and sandflats (code 1140) resulting from anthropogenic loss of the natural seabed The spatial area of loss of the habitat type reefs (code 1170) resulting from anthropogenic loss of the natural seabed The spatial area of loss of the habitat type sandbanks (code 1110) resulting from anthropogenic loss of the natural seabed The spatial area of physical disturbance to the habitat type estuaries (code 1130) The spatial area of physical disturbance to the habitat type large shallow inlets and bays (code 1160) The spatial area of physical disturbance to the habitat type mudflats and sandflats (code 1140) The spatial area of physical disturbance to the habitat type reefs (code 1170) The spatial area of physical disturbance to the habitat type sandbanks (code 1110) BALEED6C3.10 BALEED6C3.11 BALEED6C3.12 BALEED6C3.13 BALEED6C3.14 BALEED6C3.15 BALEED6C3.6 BALEED6C3.7 BALEED6C3.8 BALEED6C3.9 BALEED6C4.10 BALEED6C4.11 BALEED6C4.12 BALEED6C4.13 BALEED6C4.14 BALEED6C4.15 BALEED6C4.6 BALEED6C4.7 BALEED6C4.8 BALEED6C4.9 BALEED7C2.10 BALEED7C2.11 BALEED7C2.12 BALEED7C2.13 BALEED7C2.14 BALEED7C2.15 BALEED7C2.6 BALEED7C2.7 BALEED7C2.8 BALEED7C2.9	Spatial distibution and area of alterations of hydrographic conditions Spatial distibution and area of physical disturbance to the seabed. Spatial distibution and area of physical loss of the natural seabed The spatial area of hydrographically altered habitat type estuaries (code 1130) The spatial area of hydrographically altered habitat type large shallow inlets and bays (code 1160) The spatial area of hydrographically altered habitat type mudflats and sandflats (code 1140) The spatial area of hydrographically altered habitat type reefs (code 1170) The spatial area of hydrographically altered habitat type sandbanks (code 1110) The spatial area of loss of the habitat type estuaries (code 1130) resulting from anthropogenic loss of the natural seabed The spatial area of loss of the habitat type large shallow inlets and bays (code 1160) resulting from anthropogenic loss of the natural seabed The spatial area of loss of the habitat type mudflats and sandflats (code 1140) resulting from anthropogenic loss of the natural seabed The spatial area of loss of the habitat type reefs (code 1170) resulting from anthropogenic loss of the natural seabed The spatial area of loss of the habitat type sandbanks (code 1110) resulting from anthropogenic loss of the natural seabed The spatial area of physical disturbance to the habitat type estuaries (code 1130) The spatial area of physical disturbance to the habitat type large shallow inlets and bays (code 1160) The spatial area of physical disturbance to the habitat type mudflats and sandflats (code 1140) The spatial area of physical disturbance to the habitat type reefs (code 1170) The spatial area of physical disturbance to the habitat type sandbanks (code 1110) BALEED6C3.10 BALEED6C3.11 BALEED6C3.12 BALEED6C3.13 BALEED6C3.14 BALEED6C3.15 BALEED6C3.6 BALEED6C3.7 BALEED6C3.8 BALEED6C3.9 BALEED6C4.10 BALEED6C4.11 BALEED6C4.12 BALEED6C4.13 BALEED6C4.14 BALEED6C4.15 BALEED6C4.6 BALEED6C4.7 BALEED6C4.8 BALEED6C4.9 BALEED7C2.10 BALEED7C2.11 BALEED7C2.12 BALEED7C2.13 BALEED7C2.14 BALEED7C2.15 BALEED7C2.6 BALEED7C2.7 BALEED7C2.8 BALEED7C2.9	Spatial distibution and area of alterations of hydrographic conditions Spatial distibution and area of physical disturbance to the seabed. Spatial distibution and area of physical loss of the natural seabed The spatial area of hydrographically altered habitat type estuaries (code 1130) The spatial area of hydrographically altered habitat type large shallow inlets and bays (code 1160) The spatial area of hydrographically altered habitat type mudflats and sandflats (code 1140) The spatial area of hydrographically altered habitat type reefs (code 1170) The spatial area of hydrographically altered habitat type sandbanks (code 1110) The spatial area of loss of the habitat type estuaries (code 1130) resulting from anthropogenic loss of the natural seabed The spatial area of loss of the habitat type large shallow inlets and bays (code 1160) resulting from anthropogenic loss of the natural seabed The spatial area of loss of the habitat type mudflats and sandflats (code 1140) resulting from anthropogenic loss of the natural seabed The spatial area of loss of the habitat type reefs (code 1170) resulting from anthropogenic loss of the natural seabed The spatial area of loss of the habitat type sandbanks (code 1110) resulting from anthropogenic loss of the natural seabed The spatial area of physical disturbance to the habitat type estuaries (code 1130) The spatial area of physical disturbance to the habitat type large shallow inlets and bays (code 1160) The spatial area of physical disturbance to the habitat type mudflats and sandflats (code 1140) The spatial area of physical disturbance to the habitat type reefs (code 1170) The spatial area of physical disturbance to the habitat type sandbanks (code 1110) BALEED6C3.10 BALEED6C3.11 BALEED6C3.12 BALEED6C3.13 BALEED6C3.14 BALEED6C3.15 BALEED6C3.6 BALEED6C3.7 BALEED6C3.8 BALEED6C3.9 BALEED6C4.10 BALEED6C4.11 BALEED6C4.12 BALEED6C4.13 BALEED6C4.14 BALEED6C4.15 BALEED6C4.6 BALEED6C4.7 BALEED6C4.8 BALEED6C4.9 BALEED7C2.10 BALEED7C2.11 BALEED7C2.12 BALEED7C2.13 BALEED7C2.14 BALEED7C2.15 BALEED7C2.6 BALEED7C2.7 BALEED7C2.8 BALEED7C2.9	Spatial distibution and area of alterations of hydrographic conditions Spatial distibution and area of physical disturbance to the seabed. Spatial distibution and area of physical loss of the natural seabed The spatial area of hydrographically altered habitat type estuaries (code 1130) The spatial area of hydrographically altered habitat type large shallow inlets and bays (code 1160) The spatial area of hydrographically altered habitat type mudflats and sandflats (code 1140) The spatial area of hydrographically altered habitat type reefs (code 1170) The spatial area of hydrographically altered habitat type sandbanks (code 1110) The spatial area of loss of the habitat type estuaries (code 1130) resulting from anthropogenic loss of the natural seabed The spatial area of loss of the habitat type large shallow inlets and bays (code 1160) resulting from anthropogenic loss of the natural seabed The spatial area of loss of the habitat type mudflats and sandflats (code 1140) resulting from anthropogenic loss of the natural seabed The spatial area of loss of the habitat type reefs (code 1170) resulting from anthropogenic loss of the natural seabed The spatial area of loss of the habitat type sandbanks (code 1110) resulting from anthropogenic loss of the natural seabed The spatial area of physical disturbance to the habitat type estuaries (code 1130) The spatial area of physical disturbance to the habitat type large shallow inlets and bays (code 1160) The spatial area of physical disturbance to the habitat type mudflats and sandflats (code 1140) The spatial area of physical disturbance to the habitat type reefs (code 1170) The spatial area of physical disturbance to the habitat type sandbanks (code 1110) BALEED6C3.10 BALEED6C3.11 BALEED6C3.12 BALEED6C3.13 BALEED6C3.14 BALEED6C3.15 BALEED6C3.6 BALEED6C3.7 BALEED6C3.8 BALEED6C3.9 BALEED6C4.10 BALEED6C4.11 BALEED6C4.12 BALEED6C4.13 BALEED6C4.14 BALEED6C4.15 BALEED6C4.6 BALEED6C4.7 BALEED6C4.8 BALEED6C4.9 BALEED7C2.10 BALEED7C2.11 BALEED7C2.12 BALEED7C2.13 BALEED7C2.14 BALEED7C2.15 BALEED7C2.6 BALEED7C2.7 BALEED7C2.8 BALEED7C2.9	Spatial distibution and area of alterations of hydrographic conditions Spatial distibution and area of physical disturbance to the seabed. Spatial distibution and area of physical loss of the natural seabed The spatial area of hydrographically altered habitat type estuaries (code 1130) The spatial area of hydrographically altered habitat type large shallow inlets and bays (code 1160) The spatial area of hydrographically altered habitat type mudflats and sandflats (code 1140) The spatial area of hydrographically altered habitat type reefs (code 1170) The spatial area of hydrographically altered habitat type sandbanks (code 1110) The spatial area of loss of the habitat type estuaries (code 1130) resulting from anthropogenic loss of the natural seabed The spatial area of loss of the habitat type large shallow inlets and bays (code 1160) resulting from anthropogenic loss of the natural seabed The spatial area of loss of the habitat type mudflats and sandflats (code 1140) resulting from anthropogenic loss of the natural seabed The spatial area of loss of the habitat type reefs (code 1170) resulting from anthropogenic loss of the natural seabed The spatial area of loss of the habitat type sandbanks (code 1110) resulting from anthropogenic loss of the natural seabed The spatial area of physical disturbance to the habitat type estuaries (code 1130) The spatial area of physical disturbance to the habitat type large shallow inlets and bays (code 1160) The spatial area of physical disturbance to the habitat type mudflats and sandflats (code 1140) The spatial area of physical disturbance to the habitat type reefs (code 1170) The spatial area of physical disturbance to the habitat type sandbanks (code 1110) BALEED6C3.10 BALEED6C3.11 BALEED6C3.12 BALEED6C3.13 BALEED6C3.14 BALEED6C3.15 BALEED6C3.6 BALEED6C3.7 BALEED6C3.8 BALEED6C3.9 BALEED6C4.10 BALEED6C4.11 BALEED6C4.12 BALEED6C4.13 BALEED6C4.14 BALEED6C4.15 BALEED6C4.6 BALEED6C4.7 BALEED6C4.8 BALEED6C4.9 BALEED7C2.10 BALEED7C2.11 BALEED7C2.12 BALEED7C2.13 BALEED7C2.14 BALEED7C2.15 BALEED7C2.6 BALEED7C2.7 BALEED7C2.8 BALEED7C2.9	Oxygen debt Shallow water near-bottom oxygen conditions BALEED5C5.3	Oxygen debt Shallow water near-bottom oxygen conditions BALEED5C5.3	Oxygen debt Shallow water near-bottom oxygen conditions BALEED5C5.3	Summer-time Secchi depth transparency	Summer-time Secchi depth transparency	Summer-time Secchi depth transparency	Summer-time Secchi depth transparency	Summer-time Secchi depth transparency	Summer-time Secchi depth transparency	Summer-time Secchi depth transparency
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 Maritime Administration, Hydrography Department: Peeter Väling, peeter.valing@vta.ee; Peeter Ingerma, peeter.ingerma@vta.ee; The Geological Survey of Estonia, Department of Marine Geology and Geophysics: Sten Suuroja, sten.suuroja@egt.ee; Land Board, Geology: Ivo Sibul, ivo.sibul@maaamet.ee.	Estonian Maritime Administration, Hydrography Department: Peeter Väling, peeter.valing@vta.ee; Peeter Ingerma, peeter.ingerma@vta.ee; The Geological Survey of Estonia, Department of Marine Geology and Geophysics: Sten Suuroja, sten.suuroja@egt.ee; Land Board, Geology: Ivo Sibul, ivo.sibul@maaamet.ee.	Estonian Maritime Administration, Hydrography Department: Peeter Väling, peeter.valing@vta.ee; Peeter Ingerma, peeter.ingerma@vta.ee; The Geological Survey of Estonia, Department of Marine Geology and Geophysics: Sten Suuroja, sten.suuroja@egt.ee; Land Board, Geology: Ivo Sibul, ivo.sibul@maaamet.ee.	Estonian Maritime Administration, Hydrography Department: Peeter Väling, peeter.valing@vta.ee; Peeter Ingerma, peeter.ingerma@vta.ee; The Geological Survey of Estonia, Department of Marine Geology and Geophysics: Sten Suuroja, sten.suuroja@egt.ee; Land Board, Geology: Ivo Sibul, ivo.sibul@maaamet.ee.	The Ministry of the Environment: Kaspar Anderson, kaspar.anderson@envir.ee; Eda Andresmaa, eda.andresmaa@envir.ee); Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee.	The Ministry of the Environment: Kaspar Anderson, kaspar.anderson@envir.ee; Eda Andresmaa, eda.andresmaa@envir.ee); Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee.	The Ministry of the Environment: Kaspar Anderson, kaspar.anderson@envir.ee; Eda Andresmaa, eda.andresmaa@envir.ee); Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee.	The Ministry of the Environment: Kaspar Anderson, kaspar.anderson@envir.ee; Eda Andresmaa, eda.andresmaa@envir.ee); Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee.	The Ministry of the Environment: Kaspar Anderson, kaspar.anderson@envir.ee; Eda Andresmaa, eda.andresmaa@envir.ee); Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@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).	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).