Art11

Member State report / Art11 / 2020 / D2 / 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	D2 Non-indigenous species
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	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2
Monitoring strategy description	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".	The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities".
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Gaps and plans	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.	Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended.
Related targets	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8	Target 8
Coverage of targets	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020
Related measures	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'	BALEE-M003 - 'Increasing knowledge on non-indigenous species to control their spread' BALEE-M004 - 'Ratification and implementation of the International Convention for the Control and Management of Ships' Ballast Water and Sediments (BWMC), and participating in the regional information system' BALEE-M006 - 'Supporting the marketing/the use of limited value fish'
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	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-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact	BALEE-D00-40_MarineAndCoastalActivities BALEE-D010403-7_FishCoastal BALEE-D010403-8_FishOffshore BALEE-D010405-10_Phytop BALEE-D010405-11_Zoopl BALEE-D01040605-13_SeabedVegetationZone BALEE-D01040605-14_Macrozoobenthos BALEE-D02-18_NISRiskAreas BALEE-D02-19_NISDynImpact
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-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-7_FishCoastal	BALEE-D010403-8_FishOffshore	BALEE-D010403-8_FishOffshore	BALEE-D010403-8_FishOffshore	BALEE-D010403-8_FishOffshore	BALEE-D010403-8_FishOffshore	BALEE-D010403-8_FishOffshore	BALEE-D010403-8_FishOffshore	BALEE-D010405-10_Phytop	BALEE-D010405-10_Phytop	BALEE-D010405-10_Phytop	BALEE-D010405-11_Zoopl	BALEE-D010405-11_Zoopl	BALEE-D010405-11_Zoopl	BALEE-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-D02-18_NISRiskAreas	BALEE-D02-18_NISRiskAreas	BALEE-D02-18_NISRiskAreas	BALEE-D02-18_NISRiskAreas	BALEE-D02-19_NISDynImpact	BALEE-D02-19_NISDynImpact
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	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Coastal fish	Off-shore fish	Off-shore fish	Off-shore fish	Off-shore fish	Off-shore fish	Off-shore fish	Off-shore fish	Phytoplankton species composition, abundance and biomass	Phytoplankton species composition, abundance and biomass	Phytoplankton species composition, abundance and biomass	Zooplankton species composition, abundance and biomass	Zooplankton species composition, abundance and biomass	Zooplankton species composition, abundance and biomass	Phytobenthic communities	Phytobenthic communities	Phytobenthic communities	Phytobenthic communities	Phytobenthic communities	Phytobenthic communities	Macrozoobenthos	Macrozoobenthos	Macrozoobenthos	Macrozoobenthos	Macrozoobenthos	Macrozoobenthos	Macrozoobenthos	Macrozoobenthos	Macrozoobenthos	Non-indigenous species – harbours and adjacent regions	Non-indigenous species – harbours and adjacent regions	Non-indigenous species – harbours and adjacent regions	Non-indigenous species – harbours and adjacent regions	Non-indigenous species – abundance and biomass	Non-indigenous species – abundance and biomass
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	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	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	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-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory	BALEE-D010403-7_FishCoastal BALEE-D010403-9_FishMigratory																													BALEE-D02-18_NISRiskAreas	BALEE-D02-18_NISRiskAreas	BALEE-D02-18_NISRiskAreas	BALEE-D02-18_NISRiskAreas
Programme description	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well. The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the commercially exploited pelagic fish species – sprat and herring in the offshore areas of the Estonian marine waters. The biomass and fishing mortality of stocks are assessed. It provides data to monitoring strategy “SD1.4 Biodiversity – Fish” and „SD3-commercially exploited fish“. Monitoring is conducted annually. The program is regionally coordinated via ICES and the ICES monitoring manual is followed. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the commercially exploited pelagic fish species – sprat and herring in the offshore areas of the Estonian marine waters. The biomass and fishing mortality of stocks are assessed. It provides data to monitoring strategy “SD1.4 Biodiversity – Fish” and „SD3-commercially exploited fish“. Monitoring is conducted annually. The program is regionally coordinated via ICES and the ICES monitoring manual is followed. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the commercially exploited pelagic fish species – sprat and herring in the offshore areas of the Estonian marine waters. The biomass and fishing mortality of stocks are assessed. It provides data to monitoring strategy “SD1.4 Biodiversity – Fish” and „SD3-commercially exploited fish“. Monitoring is conducted annually. The program is regionally coordinated via ICES and the ICES monitoring manual is followed. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the commercially exploited pelagic fish species – sprat and herring in the offshore areas of the Estonian marine waters. The biomass and fishing mortality of stocks are assessed. It provides data to monitoring strategy “SD1.4 Biodiversity – Fish” and „SD3-commercially exploited fish“. Monitoring is conducted annually. The program is regionally coordinated via ICES and the ICES monitoring manual is followed. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the commercially exploited pelagic fish species – sprat and herring in the offshore areas of the Estonian marine waters. The biomass and fishing mortality of stocks are assessed. It provides data to monitoring strategy “SD1.4 Biodiversity – Fish” and „SD3-commercially exploited fish“. Monitoring is conducted annually. The program is regionally coordinated via ICES and the ICES monitoring manual is followed. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the commercially exploited pelagic fish species – sprat and herring in the offshore areas of the Estonian marine waters. The biomass and fishing mortality of stocks are assessed. It provides data to monitoring strategy “SD1.4 Biodiversity – Fish” and „SD3-commercially exploited fish“. Monitoring is conducted annually. The program is regionally coordinated via ICES and the ICES monitoring manual is followed. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor the status of the commercially exploited pelagic fish species – sprat and herring in the offshore areas of the Estonian marine waters. The biomass and fishing mortality of stocks are assessed. It provides data to monitoring strategy “SD1.4 Biodiversity – Fish” and „SD3-commercially exploited fish“. Monitoring is conducted annually. The program is regionally coordinated via ICES and the ICES monitoring manual is followed. The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental).	The aim of the programme is to monitor phytoplankton communities (species composition, abundance, biomass and seasonal cycle of dominant groups) in the water column. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD1.6 Biodiversity – pelagic habitats”, “SD4/SD1 Food webs / Biodiversity – ecosystems” and “SD2– Non-indigenous species”. The programme is related to GES Descriptor D5, Criterion D5C2, Descriptor D1, Criterion D1C6 and Descriptor D4, Criterion D4C1. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM divisions) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency of 5 to 12 times a year at the designated monitoring stations (at least 3 stations in each coastal water body and 11 in the Estonian off-shore areas). The program is regionally coordinated via HELCOM and the HELCOM monitoring manual is followed. Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). The threshold values for the indicator of seasonal succession of dominating phytoplankton groups are still missing for some assessment units of the Baltic Sea (incl. Estonian marine area), mainly due to the lack of data corresponding to the set criteria. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Pelagic habitats – community characteristics.	The aim of the programme is to monitor phytoplankton communities (species composition, abundance, biomass and seasonal cycle of dominant groups) in the water column. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD1.6 Biodiversity – pelagic habitats”, “SD4/SD1 Food webs / Biodiversity – ecosystems” and “SD2– Non-indigenous species”. The programme is related to GES Descriptor D5, Criterion D5C2, Descriptor D1, Criterion D1C6 and Descriptor D4, Criterion D4C1. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM divisions) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency of 5 to 12 times a year at the designated monitoring stations (at least 3 stations in each coastal water body and 11 in the Estonian off-shore areas). The program is regionally coordinated via HELCOM and the HELCOM monitoring manual is followed. Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). The threshold values for the indicator of seasonal succession of dominating phytoplankton groups are still missing for some assessment units of the Baltic Sea (incl. Estonian marine area), mainly due to the lack of data corresponding to the set criteria. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Pelagic habitats – community characteristics.	The aim of the programme is to monitor phytoplankton communities (species composition, abundance, biomass and seasonal cycle of dominant groups) in the water column. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD1.6 Biodiversity – pelagic habitats”, “SD4/SD1 Food webs / Biodiversity – ecosystems” and “SD2– Non-indigenous species”. The programme is related to GES Descriptor D5, Criterion D5C2, Descriptor D1, Criterion D1C6 and Descriptor D4, Criterion D4C1. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM divisions) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency of 5 to 12 times a year at the designated monitoring stations (at least 3 stations in each coastal water body and 11 in the Estonian off-shore areas). The program is regionally coordinated via HELCOM and the HELCOM monitoring manual is followed. Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). The threshold values for the indicator of seasonal succession of dominating phytoplankton groups are still missing for some assessment units of the Baltic Sea (incl. Estonian marine area), mainly due to the lack of data corresponding to the set criteria. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Pelagic habitats – community characteristics.	The aim of the programme is to monitor species composition, abundance and biomass of mesozooplankton. It provides data to monitoring strategy “SD1.6 Biodiversity – pelagic habitats”, as well as “SD2-Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptors D1, Criterion D1C6, Description D2 Criterions D2C1 and D2C2 and Descriptor D4 Criterion D4C2. Data are gathered to assess the state of the marine environment and environmental status in three coastal water bodies and all off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions) as well as pressures from/by non-indigenous species. Monitoring is conducted yearly with a frequency 10 times a year at the designated coastal monitoring stations (3 stations in each coastal water body) and with frequency twice a year for 16 stations in the Estonian off-shore areas. The program is regionally coordinated via HELCOM and the HELCOM guidelines are followed. Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). Mesozooplankton Mean Size Total Stock indicator is developed by HELCOM on the basis of mesozooplankton data. The threshold values for the indicator have been internationally agreed for some sub-basins, but not for the Gulf of Riga yet. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Pelagic habitats – community characteristics.	The aim of the programme is to monitor species composition, abundance and biomass of mesozooplankton. It provides data to monitoring strategy “SD1.6 Biodiversity – pelagic habitats”, as well as “SD2-Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptors D1, Criterion D1C6, Description D2 Criterions D2C1 and D2C2 and Descriptor D4 Criterion D4C2. Data are gathered to assess the state of the marine environment and environmental status in three coastal water bodies and all off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions) as well as pressures from/by non-indigenous species. Monitoring is conducted yearly with a frequency 10 times a year at the designated coastal monitoring stations (3 stations in each coastal water body) and with frequency twice a year for 16 stations in the Estonian off-shore areas. The program is regionally coordinated via HELCOM and the HELCOM guidelines are followed. Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). Mesozooplankton Mean Size Total Stock indicator is developed by HELCOM on the basis of mesozooplankton data. The threshold values for the indicator have been internationally agreed for some sub-basins, but not for the Gulf of Riga yet. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Pelagic habitats – community characteristics.	The aim of the programme is to monitor species composition, abundance and biomass of mesozooplankton. It provides data to monitoring strategy “SD1.6 Biodiversity – pelagic habitats”, as well as “SD2-Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptors D1, Criterion D1C6, Description D2 Criterions D2C1 and D2C2 and Descriptor D4 Criterion D4C2. Data are gathered to assess the state of the marine environment and environmental status in three coastal water bodies and all off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions) as well as pressures from/by non-indigenous species. Monitoring is conducted yearly with a frequency 10 times a year at the designated coastal monitoring stations (3 stations in each coastal water body) and with frequency twice a year for 16 stations in the Estonian off-shore areas. The program is regionally coordinated via HELCOM and the HELCOM guidelines are followed. Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). Mesozooplankton Mean Size Total Stock indicator is developed by HELCOM on the basis of mesozooplankton data. The threshold values for the indicator have been internationally agreed for some sub-basins, but not for the Gulf of Riga yet. The programme is essentially the same as in 2014, only minor changes in some monitoring stations and frequencies were undertaken. The programme corresponds to the following monitoring programmes in the indicative list: Pelagic habitats – community characteristics.	The aim of the programme is to monitor 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 monitor the occurrence and abundance/biomass of non-indigenous phytoplankton, zooplankton, macrozoobenthos and fish in harbours and adjacent areas. Port NIS monitoring is carried out in one port (Muuga) with the identified highest risk for introduction of new non-indigenous species, while monitoring of adjacent areas is performed for three harbours. In addition, species-specific monitoring covers a few most invasive non-indigenous species: the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. The programme provides data to monitoring strategy “SD2 – Non-indigenous species ”. The programme is primarily related to GES Descriptor D2, Criteria D2C1, D2C2 and D2C3; but also contributes to D1, D4 and D6. Monitoring is conducted annually at the designated monitoring stations with organism-group specific monitoring designs. The monitoring, data collection and assessment quality are assured by regional coordination via HELCOM, including following the OSPAR/HELCOM port biological monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March). The programme has been modified since 2014 by adding species-specific monitoring. The programme corresponds to the following monitoring programmes in the indicative list: Non-indigenous species inputs - from specific sources; Non-indigenous species - abundance and/or biomass.	The aim of the programme is to monitor the occurrence and abundance/biomass of non-indigenous phytoplankton, zooplankton, macrozoobenthos and fish in harbours and adjacent areas. Port NIS monitoring is carried out in one port (Muuga) with the identified highest risk for introduction of new non-indigenous species, while monitoring of adjacent areas is performed for three harbours. In addition, species-specific monitoring covers a few most invasive non-indigenous species: the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. The programme provides data to monitoring strategy “SD2 – Non-indigenous species ”. The programme is primarily related to GES Descriptor D2, Criteria D2C1, D2C2 and D2C3; but also contributes to D1, D4 and D6. Monitoring is conducted annually at the designated monitoring stations with organism-group specific monitoring designs. The monitoring, data collection and assessment quality are assured by regional coordination via HELCOM, including following the OSPAR/HELCOM port biological monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March). The programme has been modified since 2014 by adding species-specific monitoring. The programme corresponds to the following monitoring programmes in the indicative list: Non-indigenous species inputs - from specific sources; Non-indigenous species - abundance and/or biomass.	The aim of the programme is to monitor the occurrence and abundance/biomass of non-indigenous phytoplankton, zooplankton, macrozoobenthos and fish in harbours and adjacent areas. Port NIS monitoring is carried out in one port (Muuga) with the identified highest risk for introduction of new non-indigenous species, while monitoring of adjacent areas is performed for three harbours. In addition, species-specific monitoring covers a few most invasive non-indigenous species: the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. The programme provides data to monitoring strategy “SD2 – Non-indigenous species ”. The programme is primarily related to GES Descriptor D2, Criteria D2C1, D2C2 and D2C3; but also contributes to D1, D4 and D6. Monitoring is conducted annually at the designated monitoring stations with organism-group specific monitoring designs. The monitoring, data collection and assessment quality are assured by regional coordination via HELCOM, including following the OSPAR/HELCOM port biological monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March). The programme has been modified since 2014 by adding species-specific monitoring. The programme corresponds to the following monitoring programmes in the indicative list: Non-indigenous species inputs - from specific sources; Non-indigenous species - abundance and/or biomass.	The aim of the programme is to monitor the occurrence and abundance/biomass of non-indigenous phytoplankton, zooplankton, macrozoobenthos and fish in harbours and adjacent areas. Port NIS monitoring is carried out in one port (Muuga) with the identified highest risk for introduction of new non-indigenous species, while monitoring of adjacent areas is performed for three harbours. In addition, species-specific monitoring covers a few most invasive non-indigenous species: the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. The programme provides data to monitoring strategy “SD2 – Non-indigenous species ”. The programme is primarily related to GES Descriptor D2, Criteria D2C1, D2C2 and D2C3; but also contributes to D1, D4 and D6. Monitoring is conducted annually at the designated monitoring stations with organism-group specific monitoring designs. The monitoring, data collection and assessment quality are assured by regional coordination via HELCOM, including following the OSPAR/HELCOM port biological monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March). The programme has been modified since 2014 by adding species-specific monitoring. The programme corresponds to the following monitoring programmes in the indicative list: Non-indigenous species inputs - from specific sources; Non-indigenous species - abundance and/or biomass.	The aim of the programme is to cover all major organism groups (phyto/zooplankton, phyto/zoobenthos, fish) and monitor both, pelagic and benthic communities (abundance/biomass and proportion of non-indigenous species in zooplankton and macrozoobenthos communities, abundance/biomass of mobile species, and biopollution level index). Most of the data and information used originate from other monitoring strategies and programmes. The programme provides data to monitoring strategy “SD2 – Non-indigenous species ”. The programme is primarily related to GES Descriptor D2, Criteria D2C1, D2C2 and D2C3; but also contributes to D1, D4 and D6. Monitoring is conducted annually at the designated monitoring stations with organism-group specific monitoring designs. The assessment unit is the whole Estonian marine area. The monitoring and assessment quality is assured by regional coordination via HELCOM and following the HELCOM monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March). The threshold values for indicators required for MSFD assessments have been defined (nationally, except for the biopollution level). The programme corresponds to the following monitoring programmes in the indicative list: Non-indigenous species - abundance and/or biomass.	The aim of the programme is to cover all major organism groups (phyto/zooplankton, phyto/zoobenthos, fish) and monitor both, pelagic and benthic communities (abundance/biomass and proportion of non-indigenous species in zooplankton and macrozoobenthos communities, abundance/biomass of mobile species, and biopollution level index). Most of the data and information used originate from other monitoring strategies and programmes. The programme provides data to monitoring strategy “SD2 – Non-indigenous species ”. The programme is primarily related to GES Descriptor D2, Criteria D2C1, D2C2 and D2C3; but also contributes to D1, D4 and D6. Monitoring is conducted annually at the designated monitoring stations with organism-group specific monitoring designs. The assessment unit is the whole Estonian marine area. The monitoring and assessment quality is assured by regional coordination via HELCOM and following the HELCOM monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March). The threshold values for indicators required for MSFD assessments have been defined (nationally, except for the biopollution level). The programme corresponds to the following monitoring programmes in the indicative list: Non-indigenous species - abundance and/or biomass.
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	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	Effectiveness of measures Environmental state and impacts Human activities causing the pressures	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	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment
Other policies and conventions	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive Monitoring programme targeting at national legislation	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)	Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)	HELCOM Monitoring programmes Monitoring programme targeting at national legislation Water Framework Directive	HELCOM Monitoring programmes Monitoring programme targeting at national legislation Water Framework Directive	HELCOM Monitoring programmes Monitoring programme targeting at national legislation Water Framework Directive	HELCOM Monitoring programmes Habitats Directive Monitoring programme targeting at national legislation	HELCOM Monitoring programmes Habitats Directive Monitoring programme targeting at national legislation	HELCOM Monitoring programmes Habitats Directive Monitoring programme targeting at national legislation	Habitats Directive 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 IMO-BWM Invasive Alien Species Regulation Monitoring programme targeting at national legislation	Habitats Directive IMO-BWM Invasive Alien Species Regulation Monitoring programme targeting at national legislation	Habitats Directive IMO-BWM Invasive Alien Species Regulation Monitoring programme targeting at national legislation	Habitats Directive IMO-BWM Invasive Alien Species Regulation Monitoring programme targeting at national legislation	Habitats Directive IMO-BWM Invasive Alien Species Regulation Monitoring programme targeting at national legislation	Habitats Directive IMO-BWM Invasive Alien Species Regulation Monitoring programme targeting at national legislation
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	Other	Other	Other	Other	Other	Other	Other	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
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	Agreed data collection methods	Agreed data collection methods	Agreed data collection methods	Agreed data collection methods	Agreed data collection methods	Agreed data collection methods	Agreed data collection methods	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																								Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp).	For monitoring offshore fish species the hydro-acoustic surveys and scientific trawlings are carried out. In addition, ICES coordinated cruises (BIAS, BITS) are carried out and the data are submitted to the ICES database.	For monitoring offshore fish species the hydro-acoustic surveys and scientific trawlings are carried out. In addition, ICES coordinated cruises (BIAS, BITS) are carried out and the data are submitted to the ICES database.	For monitoring offshore fish species the hydro-acoustic surveys and scientific trawlings are carried out. In addition, ICES coordinated cruises (BIAS, BITS) are carried out and the data are submitted to the ICES database.	For monitoring offshore fish species the hydro-acoustic surveys and scientific trawlings are carried out. In addition, ICES coordinated cruises (BIAS, BITS) are carried out and the data are submitted to the ICES database.	For monitoring offshore fish species the hydro-acoustic surveys and scientific trawlings are carried out. In addition, ICES coordinated cruises (BIAS, BITS) are carried out and the data are submitted to the ICES database.	For monitoring offshore fish species the hydro-acoustic surveys and scientific trawlings are carried out. In addition, ICES coordinated cruises (BIAS, BITS) are carried out and the data are submitted to the ICES database.	For monitoring offshore fish species the hydro-acoustic surveys and scientific trawlings are carried out. In addition, ICES coordinated cruises (BIAS, BITS) are carried out and the data are submitted to the ICES database.	Phytoplankton samples are collected with a bathometer at water depths of 1, 5 and 10 m together with samples of seawater chlorophyll a. An integrated sample is made pooling equal amounts of water collected from fixed depths. When the integrated sample is thoroughly mixed, a portion is poured into a clear glass bottle and fixed with preservation chemical for further transport, storage and analysis of the phytoplankton sample. As part of the Ferrybox monitoring, samples are collected with an automatic sampler from depths of 4-5 m from a predefined location on the route of the liner. Phytoplankton is analysed according to the relevant international standard methods (EN 16695: 2015, HELCOM Monitoring Manual). In 3 coastal water bodies sampling is carried out annually 10-12 times per year (from April to October), Haapsalu coastal waterbody - 10-12 times every third year. Other coastal water bodies are monitored in rotation 6 times per year (from June to September) at least once during a 6-year period. In the off-shore areas the research vessel-based monitoring is conducted 5 times per year (from April to October) and 12 times every year in frames of Ferrybox monitoring.	Phytoplankton samples are collected with a bathometer at water depths of 1, 5 and 10 m together with samples of seawater chlorophyll a. An integrated sample is made pooling equal amounts of water collected from fixed depths. When the integrated sample is thoroughly mixed, a portion is poured into a clear glass bottle and fixed with preservation chemical for further transport, storage and analysis of the phytoplankton sample. As part of the Ferrybox monitoring, samples are collected with an automatic sampler from depths of 4-5 m from a predefined location on the route of the liner. Phytoplankton is analysed according to the relevant international standard methods (EN 16695: 2015, HELCOM Monitoring Manual). In 3 coastal water bodies sampling is carried out annually 10-12 times per year (from April to October), Haapsalu coastal waterbody - 10-12 times every third year. Other coastal water bodies are monitored in rotation 6 times per year (from June to September) at least once during a 6-year period. In the off-shore areas the research vessel-based monitoring is conducted 5 times per year (from April to October) and 12 times every year in frames of Ferrybox monitoring.	Phytoplankton samples are collected with a bathometer at water depths of 1, 5 and 10 m together with samples of seawater chlorophyll a. An integrated sample is made pooling equal amounts of water collected from fixed depths. When the integrated sample is thoroughly mixed, a portion is poured into a clear glass bottle and fixed with preservation chemical for further transport, storage and analysis of the phytoplankton sample. As part of the Ferrybox monitoring, samples are collected with an automatic sampler from depths of 4-5 m from a predefined location on the route of the liner. Phytoplankton is analysed according to the relevant international standard methods (EN 16695: 2015, HELCOM Monitoring Manual). In 3 coastal water bodies sampling is carried out annually 10-12 times per year (from April to October), Haapsalu coastal waterbody - 10-12 times every third year. Other coastal water bodies are monitored in rotation 6 times per year (from June to September) at least once during a 6-year period. In the off-shore areas the research vessel-based monitoring is conducted 5 times per year (from April to October) and 12 times every year in frames of Ferrybox monitoring.	The samples are collected by means of vertical hauls using a Juday or WP-2 net with 0,1 mm mesh size. The collected samples are preserved in a formaldehyde solution to microscopic analysis to be performed in a laboratory.	The samples are collected by means of vertical hauls using a Juday or WP-2 net with 0,1 mm mesh size. The collected samples are preserved in a formaldehyde solution to microscopic analysis to be performed in a laboratory.	The samples are collected by means of vertical hauls using a Juday or WP-2 net with 0,1 mm mesh size. The collected samples are preserved in a formaldehyde solution to microscopic analysis to be performed in a laboratory.	The 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.	The phytoplankton, mesozooplankton, zoobenthos, fouling, mobile epifauna and fish monitoring samples are collected in accordance with HELCOM and HELCOM/OSPAR guidelines from two ports and three adjacent areas. Information on NIS occurrence is also gathered from all biological monitoring stations.	The phytoplankton, mesozooplankton, zoobenthos, fouling, mobile epifauna and fish monitoring samples are collected in accordance with HELCOM and HELCOM/OSPAR guidelines from two ports and three adjacent areas. Information on NIS occurrence is also gathered from all biological monitoring stations.	The phytoplankton, mesozooplankton, zoobenthos, fouling, mobile epifauna and fish monitoring samples are collected in accordance with HELCOM and HELCOM/OSPAR guidelines from two ports and three adjacent areas. Information on NIS occurrence is also gathered from all biological monitoring stations.	The phytoplankton, mesozooplankton, zoobenthos, fouling, mobile epifauna and fish monitoring samples are collected in accordance with HELCOM and HELCOM/OSPAR guidelines from two ports and three adjacent areas. Information on NIS occurrence is also gathered from all biological monitoring stations.	Most of the data and information used originate from other monitoring strategies and programmes. Information on NIS occurrence is gathered from all biological monitoring stations.	Most of the data and information used originate from other monitoring strategies and programmes. Information on NIS occurrence is gathered from all biological monitoring stations.
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)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Input of litter (solid waste matter, including micro-sized litter)	Coastal fish	Coastal fish	Coastal fish	Demersal shelf fish	Demersal shelf fish	Pelagic shelf fish	Coastal fish	Coastal fish	Demersal shelf fish	Pelagic shelf fish	Coastal fish	Demersal shelf fish	Pelagic shelf fish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Coastal ecosystems	Coastal ecosystems	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Pelagic shelf fish	Pelagic shelf fish	Pelagic shelf fish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Other pelagic habitats	Coastal ecosystems	Coastal ecosystems	Other pelagic habitats	Coastal ecosystems	Coastal ecosystems	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	Newly introduced non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Newly introduced non-indigenous species	Established non-indigenous species
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			Abramis brama Alburnus alburnus Alosa fallax Ammodytes tobianus Blicca bjoerkna Carassius carassius Carassius gibelio Coregonus maraena Cyprinus carpio Esox lucius Gadus morhua Gobius niger Gymnocephalus cernua Hyperoplus lanceolatus Lampetra fluviatilis Leuciscus aspius Leuciscus idus Leuciscus leuciscus Lota lota Neogobius melanostomus Osmerus eperlanus Rutilus rutilus Scardinius erythrophthalmus Scophthalmus maximus [Psetta maxima] Squalius cephalus Tinca tinca Vimba vimba Zoarces viviparus	Anguilla anguilla	Cobitis taenia Coregonus widegreni Gobio gobio Platichthys flesus Platichthys solemdali Sander lucioperca	Cottus gobio Myoxocephalus quadricornis Myoxocephalus scorpius Taurulus bubalis	Perca fluviatilis	Belone belone Clupea harengus Coregonus albula Coregonus lavaretus Cyclopterus lumpus Pelecus cultratus Salmo salar Salmo trutta trutta Sprattus sprattus	Abramis brama Alburnus alburnus Alosa fallax Ammodytes tobianus Anguilla anguilla Blicca bjoerkna Carassius carassius Carassius gibelio Coregonus maraena Cyprinus carpio Esox lucius Gadus morhua Gobius niger Gymnocephalus cernua Hyperoplus lanceolatus Lampetra fluviatilis Leuciscus aspius Leuciscus idus Leuciscus leuciscus Lota lota Neogobius melanostomus Osmerus eperlanus Rutilus rutilus Scardinius erythrophthalmus Scophthalmus maximus [Psetta maxima] Squalius cephalus Tinca tinca Vimba vimba Zoarces viviparus	Cobitis taenia Coregonus widegreni Gobio gobio Platichthys flesus Platichthys solemdali Sander lucioperca	Cottus gobio Myoxocephalus quadricornis Myoxocephalus scorpius Perca fluviatilis Taurulus bubalis	Belone belone Clupea harengus Coregonus albula Coregonus lavaretus Cyclopterus lumpus Pelecus cultratus Salmo salar Salmo trutta trutta Sprattus sprattus	Cobitis taenia	Cottus gobio	Coregonus lavaretus	Clupea harengus	Perca fluviatilis Platichthys flesus Platichthys solemdali Sander lucioperca	Clupea harengus	Perca fluviatilis Platichthys flesus Platichthys solemdali Salmo salar Sander lucioperca	Clupea harengus	Perca fluviatilis Platichthys flesus Platichthys solemdali	Salmo salar	Sander lucioperca	Fish community	Fish community		Clupea harengus Sprattus sprattus	Clupea harengus Sprattus sprattus	Clupea harengus Sprattus sprattus	Clupea harengus Sprattus sprattus	Clupea harengus Sprattus sprattus	Clupea harengus Sprattus sprattus	Phytoplankton communities	Primary producers	Primary producers	Zooplankton communities	All trophic guilds Secondary producers	All trophic guilds Secondary producers	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 - macrobenthic communities Benthic habitats - macrophyte communities Zooplankton communities	Eriocheir sinensis Neogobius melanostomus Rhithropanopeus harrisii	Fouling Mobile epifauna Phytoplankton communities	Not Applicable	Eriocheir sinensis Neogobius melanostomus Rhithropanopeus harrisii
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			D1C2	D1C2	D1C2	D1C2	D1C2	D1C2	D1C3	D1C3	D1C3	D1C3	D1C4	D1C4	D1C4	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C3	D3C3	D4C1	D4C2		D1C1	D1C2	D1C3	D3C1	D3C2	D3C3	D1C6	D4C1	D4C2	D1C6	D4C1	D4C2	D10C1	D2C1	D2C2	D5C6	D5C7	D6C5	D2C1	D2C2	D2C3	D4C1	D4C2	D4C2	D5C8	D6C4	D6C5	D2C1	D2C2	D2C2	D2C2	D2C1	D2C2
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			Abundance (number of individuals) Other	Abundance (number of individuals) Other	Abundance (number of individuals) Biomass Other	Abundance (number of individuals) Other	Abundance (number of individuals) Biomass Other	Abundance (number of individuals) Other	Age distribution Length Sex distribution	Age distribution Length Sex distribution	Age distribution Length Sex distribution	Age distribution Length Sex distribution	Distribution (spatial)	Distribution (spatial)	Distribution (spatial)	Mortality rate	Other	Abundance (number of individuals) Biomass of Spawning Stock (SSB)	Abundance (number of individuals) Other	Other	Length Other	Length	Length Other	Other	Abundance (number of individuals) Other		Mortality rate	Abundance (number of individuals) Biomass	Age distribution	Mortality rate	Abundance (number of individuals) Biomass of Spawning Stock (SSB)	Other	Other	Other	Abundance (number of individuals) Biomass	Other	Other	Abundance (number of individuals) Biomass	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	Abundance (number of individuals) Biomass Other	Abundance (number of individuals) Biomass	Abundance (number of individuals) Biomass Other	Other	Abundance (number of individuals) Biomass
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			Mass (catch weight per unit effort)	Abundance index of European eel in monitoring catc	Mass (catch weight per unit effort)	Mass (catch weight per unit effort)	Mass (catch weight per unit effort)	Mass (catch weight per unit effort)	Mass (catch weight per unit effort)	Mass (catch mass per unit effort)	Mass (catch mass per unit effort)	Mass (catch mass per unit effort)					Ratio between annual commercial catch and biomass		Mass (commercial catch weight per unit effort)	Age distribution	Age distribution; Sex distribution	Mass (commercial catch weight per unit effort)	Sex distribution; Age distribution	Species composition; Trophic level class of fish s	Abundance of coastal fish key functional groups (C							Age distribution	Species composition; Abundance (number of individu	Species composition		Species composition; Abundance (number of individu	Species composition			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	Species composition; Abundance (number of individu	Species composition; Relative biomass in community		Species composition	Species composition; Abundance (number of individu	Species composition
Spatial scope	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) 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	EEZ (or similar) Territorial waters	EEZ (or similar) Territorial waters	EEZ (or similar) Territorial waters	EEZ (or similar) Territorial waters	EEZ (or similar) Territorial waters	EEZ (or similar) Territorial waters	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)	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
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-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GR BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 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-GF-EE-ICES_SD_32 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-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP BAL-EGB-EE-EEEE_11 BAL-GF-EE-EEEE_01 BAL-GF-EE-EEEE_02 BAL-GF-EE-EEEE_03 BAL-GF-EE-EEEE_05 BAL-GF-EE-EEEE_06 BAL-GR-EE-EEEE_07 BAL-GR-EE-EEEE_08 BAL-GR-EE-EEEE_09 BAL-GR-EE-EEEE_13 BAL-GR-EE-EEEE_14 BAL-GR-EE-EEEE_16 BAL-GR-EE-EEEE_17 BAL-GR-EE-EEEE_18 BAL-GR-EE-EEEE_19 BAL-NBP-EE-EEEE_10	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP BAL-EGB-EE-EEEE_11 BAL-GF-EE-EEEE_01 BAL-GF-EE-EEEE_02 BAL-GF-EE-EEEE_03 BAL-GF-EE-EEEE_05 BAL-GF-EE-EEEE_06 BAL-GR-EE-EEEE_07 BAL-GR-EE-EEEE_08 BAL-GR-EE-EEEE_09 BAL-GR-EE-EEEE_13 BAL-GR-EE-EEEE_14 BAL-GR-EE-EEEE_16 BAL-GR-EE-EEEE_17 BAL-GR-EE-EEEE_18 BAL-GR-EE-EEEE_19 BAL-NBP-EE-EEEE_10	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP BAL-EGB-EE-EEEE_11 BAL-GF-EE-EEEE_01 BAL-GF-EE-EEEE_02 BAL-GF-EE-EEEE_03 BAL-GF-EE-EEEE_05 BAL-GF-EE-EEEE_06 BAL-GR-EE-EEEE_07 BAL-GR-EE-EEEE_08 BAL-GR-EE-EEEE_09 BAL-GR-EE-EEEE_13 BAL-GR-EE-EEEE_14 BAL-GR-EE-EEEE_16 BAL-GR-EE-EEEE_17 BAL-GR-EE-EEEE_18 BAL-GR-EE-EEEE_19 BAL-NBP-EE-EEEE_10	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP BAL-EGB-EE-EEEE_11 BAL-GF-EE-EEEE_01 BAL-GF-EE-EEEE_02 BAL-GF-EE-EEEE_03 BAL-GF-EE-EEEE_05 BAL-GF-EE-EEEE_06 BAL-GR-EE-EEEE_07 BAL-GR-EE-EEEE_08 BAL-GR-EE-EEEE_09 BAL-GR-EE-EEEE_13 BAL-GR-EE-EEEE_14 BAL-GR-EE-EEEE_16 BAL-GR-EE-EEEE_17 BAL-GR-EE-EEEE_18 BAL-GR-EE-EEEE_19 BAL-NBP-EE-EEEE_10	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP BAL-EGB-EE-EEEE_11 BAL-GF-EE-EEEE_01 BAL-GF-EE-EEEE_02 BAL-GF-EE-EEEE_03 BAL-GF-EE-EEEE_05 BAL-GF-EE-EEEE_06 BAL-GR-EE-EEEE_07 BAL-GR-EE-EEEE_08 BAL-GR-EE-EEEE_09 BAL-GR-EE-EEEE_13 BAL-GR-EE-EEEE_14 BAL-GR-EE-EEEE_16 BAL-GR-EE-EEEE_17 BAL-GR-EE-EEEE_18 BAL-GR-EE-EEEE_19 BAL-NBP-EE-EEEE_10	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP BAL-EGB-EE-EEEE_11 BAL-GF-EE-EEEE_01 BAL-GF-EE-EEEE_02 BAL-GF-EE-EEEE_03 BAL-GF-EE-EEEE_05 BAL-GF-EE-EEEE_06 BAL-GR-EE-EEEE_07 BAL-GR-EE-EEEE_08 BAL-GR-EE-EEEE_09 BAL-GR-EE-EEEE_13 BAL-GR-EE-EEEE_14 BAL-GR-EE-EEEE_16 BAL-GR-EE-EEEE_17 BAL-GR-EE-EEEE_18 BAL-GR-EE-EEEE_19 BAL-NBP-EE-EEEE_10	BAL-EE-AA BAL-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-GF-EE-EEEE_01 BAL-GF-EE-EEEE_05 BAL-GR-EE-EEEE_13	BAL-EE-AA BAL-GF-EE-EEEE_01 BAL-GF-EE-EEEE_05 BAL-GR-EE-EEEE_13	BAL-EE-AA BAL-GF-EE-EEEE_01 BAL-GF-EE-EEEE_05 BAL-GR-EE-EEEE_13	BAL-EE-AA BAL-GF-EE-EEEE_01 BAL-GF-EE-EEEE_05 BAL-GR-EE-EEEE_13	BAL-EE-AA BAL-EE-GF BAL-EE-GR BAL-EE-NBP BAL-GF-EE-EEEE_01 BAL-GF-EE-EEEE_05 BAL-GR-EE-EEEE_13	BAL-EE-AA BAL-EE-GF BAL-EE-GR BAL-EE-NBP BAL-GF-EE-EEEE_01 BAL-GF-EE-EEEE_05 BAL-GR-EE-EEEE_13
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	1975-9999	1975-9999	1975-9999	1975-9999	1975-9999	1975-9999	1975-9999	1975-9999	1975-9999	1975-9999	1975-9999	1975-9999	1975-9999	1975-9999	1975-9999	1975-9999	1975-9999	1975-9999	1975-9999	1975-9999	1975-9999	1975-9999	1975-9999	1975-9999	1975-9999	1992-9999	1992-9999	1992-9999	1992-9999	1992-9999	1992-9999	1992-9999	1993-9999	1993-9999	1993-9999	1993-9999	1993-9999	1993-9999	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	2010-9999	2010-9999	2010-9999	2010-9999	2010-9999	2010-9999
Monitoring frequency	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	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	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	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	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 offshore	In-situ sampling offshore	In-situ sampling offshore	In-situ sampling offshore	In-situ sampling offshore	In-situ sampling offshore	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 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 coastal	In-situ sampling coastal	In-situ sampling coastal	In-situ sampling coastal Numerical modelling	In-situ sampling coastal Numerical modelling
Monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	HELCOM Guidelines for coastal fish monitoring Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	HELCOM Guidelines for monitoring phytoplankton species composition, abundance and biomass	HELCOM Guidelines for monitoring phytoplankton species composition, abundance and biomass	HELCOM Guidelines for monitoring phytoplankton species composition, abundance and biomass	HELCOM Guidelines for monitoring of mesozooplankton	HELCOM Guidelines for monitoring of mesozooplankton	HELCOM Guidelines for monitoring of mesozooplankton	HELCOM 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	HELCOM Guidelines for monitoring of mesozooplankton HELCOM Guidelines for monitoring of non-indigenous species by eRAS HELCOM Guidelines for monitoring phytoplankton species composition, abundance and biomass OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) Other monitoring method	HELCOM Guidelines for monitoring of mesozooplankton HELCOM Guidelines for monitoring of non-indigenous species by eRAS HELCOM Guidelines for monitoring phytoplankton species composition, abundance and biomass OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) Other monitoring method	HELCOM Guidelines for monitoring of mesozooplankton HELCOM Guidelines for monitoring of non-indigenous species by eRAS HELCOM Guidelines for monitoring phytoplankton species composition, abundance and biomass OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) Other monitoring method	HELCOM Guidelines for monitoring of mesozooplankton HELCOM Guidelines for monitoring of non-indigenous species by eRAS HELCOM Guidelines for monitoring phytoplankton species composition, abundance and biomass OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) Other monitoring method	Other monitoring method	Other monitoring method
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.	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	The monitoring and assessment of the state of herring and sprat stocks are following the ICES WGBFAS methodology. Herring and sprat stocks and stock trends are assessed on the basis of the catches. Based on the collected material, biological analyses are performed and the age of the individuals is determined.	The monitoring and assessment of the state of herring and sprat stocks are following the ICES WGBFAS methodology. Herring and sprat stocks and stock trends are assessed on the basis of the catches. Based on the collected material, biological analyses are performed and the age of the individuals is determined.	The monitoring and assessment of the state of herring and sprat stocks are following the ICES WGBFAS methodology. Herring and sprat stocks and stock trends are assessed on the basis of the catches. Based on the collected material, biological analyses are performed and the age of the individuals is determined.	The monitoring and assessment of the state of herring and sprat stocks are following the ICES WGBFAS methodology. Herring and sprat stocks and stock trends are assessed on the basis of the catches. Based on the collected material, biological analyses are performed and the age of the individuals is determined.	The monitoring and assessment of the state of herring and sprat stocks are following the ICES WGBFAS methodology. Herring and sprat stocks and stock trends are assessed on the basis of the catches. Based on the collected material, biological analyses are performed and the age of the individuals is determined.	The monitoring and assessment of the state of herring and sprat stocks are following the ICES WGBFAS methodology. Herring and sprat stocks and stock trends are assessed on the basis of the catches. Based on the collected material, biological analyses are performed and the age of the individuals is determined.	The monitoring and assessment of the state of herring and sprat stocks are following the ICES WGBFAS methodology. Herring and sprat stocks and stock trends are assessed on the basis of the catches. Based on the collected material, biological analyses are performed and the age of the individuals is determined.													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	Joint HELCOM/OSPAR Guidelines on the granting of exemptions under the International Convention for the Control and Management of Ships’ Ballast Water and Sediments, Regulation A (https://www.helcom.fi/wp-content/uploads/2019/08/Joint-HELCOM_OSPAR-Guidelines.pdf);	Joint HELCOM/OSPAR Guidelines on the granting of exemptions under the International Convention for the Control and Management of Ships’ Ballast Water and Sediments, Regulation A (https://www.helcom.fi/wp-content/uploads/2019/08/Joint-HELCOM_OSPAR-Guidelines.pdf);	Joint HELCOM/OSPAR Guidelines on the granting of exemptions under the International Convention for the Control and Management of Ships’ Ballast Water and Sediments, Regulation A (https://www.helcom.fi/wp-content/uploads/2019/08/Joint-HELCOM_OSPAR-Guidelines.pdf);	Joint HELCOM/OSPAR Guidelines on the granting of exemptions under the International Convention for the Control and Management of Ships’ Ballast Water and Sediments, Regulation A (https://www.helcom.fi/wp-content/uploads/2019/08/Joint-HELCOM_OSPAR-Guidelines.pdf);	The numerical data used are calculated on the basis of data collected under other programmes. The level of biopollution is assessed on the basis of a scientifically validated methodology (Olenin et al. 2007) for an average of three sub-basins (the Gulf of Riga, the Gulf of Finland and the Baltic Proper).	The numerical data used are calculated on the basis of data collected under other programmes. The level of biopollution is assessed on the basis of a scientifically validated methodology (Olenin et al. 2007) for an average of three sub-basins (the Gulf of Riga, the Gulf of Finland and the Baltic Proper).
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 the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS).	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	ICES WGBFAS	The quality is ensured by following the standard methods and HELCOM guidance as well as accreditation of experts and persons by whom the monitoring is performed.	The quality is ensured by following the standard methods and HELCOM guidance as well as accreditation of experts and persons by whom the monitoring is performed.	The quality is ensured by following the standard methods and HELCOM guidance as well as accreditation of experts and persons by whom the monitoring is performed.	The quality is ensured by following the HELCOM guidance as well as accreditation of experts and persons by whom the monitoring is performed.	The quality is ensured by following the HELCOM guidance as well as accreditation of experts and persons by whom the monitoring is performed.	The quality is ensured by following the HELCOM guidance as well as accreditation of experts and persons by whom the monitoring is performed.	The quality is ensured by 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 is ensured by the accreditation of experts and persons by whom the monitoring is performed and following guidance recommendations.	The quality is ensured by the accreditation of experts and persons by whom the monitoring is performed and following guidance recommendations.	The quality is ensured by the accreditation of experts and persons by whom the monitoring is performed and following guidance recommendations.	The quality is ensured by the accreditation of experts and persons by whom the monitoring is performed and following guidance recommendations.	The monitoring and assessment quality is assured by regional coordination via HELCOM, following the HELCOM, HELCOM/OSPAR and national monitoring guidelines, and accreditation of experts and persons by whom the monitoring is performed.	The monitoring and assessment quality is assured by regional coordination via HELCOM, following the HELCOM, HELCOM/OSPAR and national monitoring guidelines, and accreditation of experts and persons by whom the monitoring is performed.
Data management	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University.	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).	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).	Data are yearly reported to the national environmental monitoring database KESE (by 1 March).	Data are yearly reported to the national environmental monitoring database KESE (by 1 March).	Data are yearly reported to the national environmental monitoring database KESE (by 1 March).	Data are yearly reported to the national environmental monitoring database KESE (by 1 March).	The data are yearly reported to the national environmental monitoring database KESE (by 1 March).	The data are yearly reported to the national environmental monitoring database KESE (by 1 March).
Data 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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://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded	https://www.agri.ee/et/eesmargid-tegevused/kalamajandus-ja-kutseline-kalapuuk/puugiandmed,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Related indicator/name																								95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	95 % percentile of the length distribution of flounder (Platichthys flesus) in monitoring catches 95 % percentile of the length distribution of pikeperch (Sander lucioperca) in monitoring catches Abundance index of large(TL>250 mm) perch (Perca fluviatilis) in monitoring catches Abundance index of sexually mature female pikeperch (Sander lucioperca) in monitoring catches Abundance index of sexually mature flounder (Platichthys flesus) in monitoring catches Abundance index of sexually mature perch (Perca fluviatilis) in monitoring catches Abundance of coastal Fish key functional groups: abundance of cyprinids in monitoring catches Abundance of coastal Fish key functional groups: abundance of piscivores in monitoring catches Fish community trophic index Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga Mean maximum length across all fish species found in monitoring catches (MMLI) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of flounder (Platichthys flesus) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of perch (Perca fluviatilis) Ratio between annual commercial catch and biomass index (WPUE in monitoring area) of pikeperch (Sander lucioperca) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Gulf of Riga The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis The smolt production of Baltic salmon (Salmo salar) relative to the level of natural smolt production capacity on a riverby river basis BALEED1C2.5 BALEED1C4.5 BALEED1C4.6 BALEED1C4.7	Fishing mortality (F) of Baltic sprat (Sprattus sprattus balticus) Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Estonian marine areas (ICES subregions SD 27-29, 32) Spawning stock biomass (SSB) of Baltic sprat (Sprattus sprattus balticus) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Estonian marine areas (ICES subregions SD 27-29, 32)	Fishing mortality (F) of Baltic sprat (Sprattus sprattus balticus) Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Estonian marine areas (ICES subregions SD 27-29, 32) Spawning stock biomass (SSB) of Baltic sprat (Sprattus sprattus balticus) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Estonian marine areas (ICES subregions SD 27-29, 32)	Fishing mortality (F) of Baltic sprat (Sprattus sprattus balticus) Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Estonian marine areas (ICES subregions SD 27-29, 32) Spawning stock biomass (SSB) of Baltic sprat (Sprattus sprattus balticus) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Estonian marine areas (ICES subregions SD 27-29, 32)	Fishing mortality (F) of Baltic sprat (Sprattus sprattus balticus) Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Estonian marine areas (ICES subregions SD 27-29, 32) Spawning stock biomass (SSB) of Baltic sprat (Sprattus sprattus balticus) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Estonian marine areas (ICES subregions SD 27-29, 32)	Fishing mortality (F) of Baltic sprat (Sprattus sprattus balticus) Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Estonian marine areas (ICES subregions SD 27-29, 32) Spawning stock biomass (SSB) of Baltic sprat (Sprattus sprattus balticus) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Estonian marine areas (ICES subregions SD 27-29, 32)	Fishing mortality (F) of Baltic sprat (Sprattus sprattus balticus) Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Estonian marine areas (ICES subregions SD 27-29, 32) Spawning stock biomass (SSB) of Baltic sprat (Sprattus sprattus balticus) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Estonian marine areas (ICES subregions SD 27-29, 32)	Fishing mortality (F) of Baltic sprat (Sprattus sprattus balticus) Fishing mortality (F) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Estonian marine areas (ICES subregions SD 27-29, 32) Spawning stock biomass (SSB) of Baltic sprat (Sprattus sprattus balticus) Spawning stock biomass (SSB) of subpopulation of spring spawning baltic herring (Clupea harengus membras) in Estonian marine areas (ICES subregions SD 27-29, 32)	Seasonal succession of dominating phytoplankton groups Summer phytoplankton wet weight biomass	Seasonal succession of dominating phytoplankton groups Summer phytoplankton wet weight biomass	Seasonal succession of dominating phytoplankton groups Summer phytoplankton wet weight biomass	Zooplankton mean size and total stock	Zooplankton mean size and total stock	Zooplankton mean size and total stock	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	Abundance of alien pelagic invertebrate species Biomass of alien benthic invertebrate species Catch per unit effort of mobile non-indigenous species Contribution of non-indigenous species in macrozoobenthic community Contribution of non-indigenous species in zooplankton community Number of new non-indigenous species	Abundance of alien pelagic invertebrate species Biomass of alien benthic invertebrate species Catch per unit effort of mobile non-indigenous species Contribution of non-indigenous species in macrozoobenthic community Contribution of non-indigenous species in zooplankton community Number of new non-indigenous species	Abundance of alien pelagic invertebrate species Biomass of alien benthic invertebrate species Catch per unit effort of mobile non-indigenous species Contribution of non-indigenous species in macrozoobenthic community Contribution of non-indigenous species in zooplankton community Number of new non-indigenous species	Abundance of alien pelagic invertebrate species Biomass of alien benthic invertebrate species Catch per unit effort of mobile non-indigenous species Contribution of non-indigenous species in macrozoobenthic community Contribution of non-indigenous species in zooplankton community Number of new non-indigenous species	Abundance of alien pelagic invertebrate species Biomass of alien benthic invertebrate species Biopollution level (BPL) Catch per unit effort of mobile non-indigenous species Contribution of non-indigenous species in macrozoobenthic community Contribution of non-indigenous species in zooplankton community Number of new non-indigenous species	Abundance of alien pelagic invertebrate species Biomass of alien benthic invertebrate species Biopollution level (BPL) Catch per unit effort of mobile non-indigenous species Contribution of non-indigenous species in macrozoobenthic community Contribution of non-indigenous species in zooplankton community Number of new non-indigenous species
Contact																								Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee); University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee.	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
References	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	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).