Member State report / Art11 / 2020 / D1-B / Finland / Baltic Sea

Report type Member State report to Commission
MSFD Article Art. 11 Monitoring programmes (and Art. 17 updates)
Report due 2020-10-15
GES Descriptor D1 Birds
Member State Finland
Region/subregion Baltic Sea
Reported by Finnish Environment Institute
Report date 2020-10-31
Report access

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Monitoring strategy description
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
Coverage of GES criteria
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Gaps and plans
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
Related targets
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
Coverage of targets
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Related measures
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
Coverage of measures
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Related monitoring programmes
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
Programme code
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-2
BALFI-D01,04,06bir-2
BALFI-D01,04,06bir-2
BALFI-D01,04,06bir-2
BALFI-D01,04,06bir-2
BALFI-D01,04,06bir-2
BALFI-D01,04,06bir-2
BALFI-D01,04,06bir-2
BALFI-D01,04,06bir-4
BALFI-D01,04,06bir-4
BALFI-D01,04,06bir-4
BALFI-D01,04,06bir-4
BALFI-D03-2
BALFI-D03-2
BALFI-D03-2
BALFI-D03-2
BALFI-D03-2
BALFI-D03-2
BALFI-D03-2
BALFI-D03-2
BALFI-D03-2
BALFI-D03-2
BALFI-D03-2
BALFI-d01,04,06bir-3
BALFI-d01,04,06bir-3
BALFI-d01,04,06bir-5
BALFI-d01,04,06bir-5
BALFI-d01,04,06bir-5
BALFI-d01,04,06bir-5
Programme name
Marine breeding birds
Marine breeding birds
Marine breeding birds
Marine breeding birds
Marine breeding birds
Marine breeding birds
Marine breeding birds
Marine breeding birds
Marine breeding birds
Marine breeding birds
Marine breeding birds
Marine wintering birds
Marine wintering birds
Marine wintering birds
Marine wintering birds
Marine wintering birds
Marine wintering birds
Marine wintering birds
Marine wintering birds
White tailed eagle breeding success
White tailed eagle breeding success
White tailed eagle breeding success
White tailed eagle breeding success
Commercial fisheries catch statistics
Commercial fisheries catch statistics
Commercial fisheries catch statistics
Commercial fisheries catch statistics
Commercial fisheries catch statistics
Commercial fisheries catch statistics
Commercial fisheries catch statistics
Commercial fisheries catch statistics
Commercial fisheries catch statistics
Commercial fisheries catch statistics
Commercial fisheries catch statistics
Mass mortalities of breeding sea birds
Mass mortalities of breeding sea birds
Hunting of sea birds and seals
Hunting of sea birds and seals
Hunting of sea birds and seals
Hunting of sea birds and seals
Update type
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
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Old programme codes
Programme description
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Wintering birds monitoring and data collection on species numbers, abundance and distribution.Work cordinated by HELCOM in Baltic Sea area.
Wintering birds monitoring and data collection on species numbers, abundance and distribution.Work cordinated by HELCOM in Baltic Sea area.
Wintering birds monitoring and data collection on species numbers, abundance and distribution.Work cordinated by HELCOM in Baltic Sea area.
Wintering birds monitoring and data collection on species numbers, abundance and distribution.Work cordinated by HELCOM in Baltic Sea area.
Wintering birds monitoring and data collection on species numbers, abundance and distribution.Work cordinated by HELCOM in Baltic Sea area.
Wintering birds monitoring and data collection on species numbers, abundance and distribution.Work cordinated by HELCOM in Baltic Sea area.
Wintering birds monitoring and data collection on species numbers, abundance and distribution.Work cordinated by HELCOM in Baltic Sea area.
Wintering birds monitoring and data collection on species numbers, abundance and distribution.Work cordinated by HELCOM in Baltic Sea area.
White tailed eagle breeding success monitoring is largely based on volunteers coordinated by Sääksisäätiö-nonprofit organisation
White tailed eagle breeding success monitoring is largely based on volunteers coordinated by Sääksisäätiö-nonprofit organisation
White tailed eagle breeding success monitoring is largely based on volunteers coordinated by Sääksisäätiö-nonprofit organisation
White tailed eagle breeding success monitoring is largely based on volunteers coordinated by Sääksisäätiö-nonprofit organisation
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
Mass mortalities of breeding sea birds are monitored in the vicinity of breeding colonies. Therefore the monitoring is focuses on islands and islets in coastal and territorial waters. Aim is to register number of mass mortality's and causes
Mass mortalities of breeding sea birds are monitored in the vicinity of breeding colonies. Therefore the monitoring is focuses on islands and islets in coastal and territorial waters. Aim is to register number of mass mortality's and causes
Hunting of sea birds and seals is practiced in coastal and territorial waters according to hunting regulations.Hunting organizations carry out game questionnaires. Hunting statistics are maintained by the hunting organizations and stored into a database. Data on species requiring special permit is obtained through the licensing system.
Hunting of sea birds and seals is practiced in coastal and territorial waters according to hunting regulations.Hunting organizations carry out game questionnaires. Hunting statistics are maintained by the hunting organizations and stored into a database. Data on species requiring special permit is obtained through the licensing system.
Hunting of sea birds and seals is practiced in coastal and territorial waters according to hunting regulations.Hunting organizations carry out game questionnaires. Hunting statistics are maintained by the hunting organizations and stored into a database. Data on species requiring special permit is obtained through the licensing system.
Hunting of sea birds and seals is practiced in coastal and territorial waters according to hunting regulations.Hunting organizations carry out game questionnaires. Hunting statistics are maintained by the hunting organizations and stored into a database. Data on species requiring special permit is obtained through the licensing system.
Monitoring purpose
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Environmental state and impacts
  • Environmental state and impacts
  • Human activities causing the pressures
  • Human activities causing the pressures
  • Human activities causing the pressures
  • Human activities causing the pressures
Other policies and conventions
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • AEWA
  • Birds Directive
  • HELCOM Monitoring programmes
  • AEWA
  • Birds Directive
  • HELCOM Monitoring programmes
  • AEWA
  • Birds Directive
  • HELCOM Monitoring programmes
  • AEWA
  • Birds Directive
  • HELCOM Monitoring programmes
  • AEWA
  • Birds Directive
  • HELCOM Monitoring programmes
  • AEWA
  • Birds Directive
  • HELCOM Monitoring programmes
  • AEWA
  • Birds Directive
  • HELCOM Monitoring programmes
  • AEWA
  • Birds Directive
  • HELCOM Monitoring programmes
  • Birds Directive
  • HELCOM Monitoring programmes
  • Birds Directive
  • HELCOM Monitoring programmes
  • Birds Directive
  • HELCOM Monitoring programmes
  • Birds Directive
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Birds Directive
  • Birds Directive
  • Birds Directive
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
Regional cooperation - coordinating body
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
Regional cooperation - countries involved
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
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
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
Agreed data collection methods
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
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
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Monitoring details
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Methods for flight monitoring are agreed upon by Baltic sea countries on HELCOM (HELCOM 2015). Coastal monitoring is carried out by onshore observers. Offshore monitoring is carried out by boat and airplane.
Methods for flight monitoring are agreed upon by Baltic sea countries on HELCOM (HELCOM 2015). Coastal monitoring is carried out by onshore observers. Offshore monitoring is carried out by boat and airplane.
Methods for flight monitoring are agreed upon by Baltic sea countries on HELCOM (HELCOM 2015). Coastal monitoring is carried out by onshore observers. Offshore monitoring is carried out by boat and airplane.
Methods for flight monitoring are agreed upon by Baltic sea countries on HELCOM (HELCOM 2015). Coastal monitoring is carried out by onshore observers. Offshore monitoring is carried out by boat and airplane.
Methods for flight monitoring are agreed upon by Baltic sea countries on HELCOM (HELCOM 2015). Coastal monitoring is carried out by onshore observers. Offshore monitoring is carried out by boat and airplane.
Methods for flight monitoring are agreed upon by Baltic sea countries on HELCOM (HELCOM 2015). Coastal monitoring is carried out by onshore observers. Offshore monitoring is carried out by boat and airplane.
Methods for flight monitoring are agreed upon by Baltic sea countries on HELCOM (HELCOM 2015). Coastal monitoring is carried out by onshore observers. Offshore monitoring is carried out by boat and airplane.
Methods for flight monitoring are agreed upon by Baltic sea countries on HELCOM (HELCOM 2015). Coastal monitoring is carried out by onshore observers. Offshore monitoring is carried out by boat and airplane.
https://helcom.fi/wp-content/uploads/2019/12/Birds-Marine-bird-health.pdf
https://helcom.fi/wp-content/uploads/2019/12/Birds-Marine-bird-health.pdf
https://helcom.fi/wp-content/uploads/2019/12/Birds-Marine-bird-health.pdf
https://helcom.fi/wp-content/uploads/2019/12/Birds-Marine-bird-health.pdf
Fishermens’ reporting to authorities.
Fishermens’ reporting to authorities.
Fishermens’ reporting to authorities.
Fishermens’ reporting to authorities.
Fishermens’ reporting to authorities.
Fishermens’ reporting to authorities.
Fishermens’ reporting to authorities.
Fishermens’ reporting to authorities.
Fishermens’ reporting to authorities.
Fishermens’ reporting to authorities.
Fishermens’ reporting to authorities.
The sub-programme collects data on mass deaths of seabirds. Information can be obtained from different clubs and other sources of information, in particular public and amateur observations. The aim is to identify the number of mass deaths of seabirds and to identify the causes of death. This is, as a general rule, “passive” monitoring, i.e. information obtained through other activities and monitoring.
The sub-programme collects data on mass deaths of seabirds. Information can be obtained from different clubs and other sources of information, in particular public and amateur observations. The aim is to identify the number of mass deaths of seabirds and to identify the causes of death. This is, as a general rule, “passive” monitoring, i.e. information obtained through other activities and monitoring.
Features
Grazing birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Wading birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Wading birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Disturbance of species (e.g. where they breed, rest and feed) due to human presence
Surface-feeding birds
Disturbance of species (e.g. where they breed, rest and feed) due to human presence
Adverse effects on species or habitats
Benthic-feeding birds
Pelagic-feeding birds
Surface-feeding birds
Small toothed cetaceans
Seals
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Coastal ecosystems
Coastal ecosystems
Fish and shellfish harvesting (professional, recreational)
Pelagic-feeding birds
Surface-feeding birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Seals
Elements
  • Branta leucopsis
  • Aythya fuligula
  • Aythya marila
  • Melanitta fusca
  • Somateria mollissima
  • Anser anser
  • Branta leucopsis
  • Cygnus olor
  • Alca torda
  • Cepphus grylle
  • Mergus merganser
  • Mergus serrator
  • Phalacrocorax carbo
  • Podiceps cristatus
  • Uria aalge
  • Hydroprogne caspia
  • Larus argentatus
  • Larus canus
  • Larus marinus
  • Stercorarius parasiticus
  • Sterna hirundo
  • Sterna paradisaea
  • Sterna sandvicensis
  • Sternula albifrons
  • Arenaria interpres
  • Calidris alpina
  • Charadrius hiaticula
  • Haematopus ostralegus
  • Larus fuscus
  • Tadorna tadorna
  • Aythya fuligula
  • Aythya marila
  • Melanitta fusca
  • Somateria mollissima
  • Anser anser
  • Branta leucopsis
  • Cygnus olor
  • Alca torda
  • Cepphus grylle
  • Mergus merganser
  • Mergus serrator
  • Phalacrocorax carbo
  • Podiceps cristatus
  • Uria aalge
  • Hydroprogne caspia
  • Larus argentatus
  • Larus canus
  • Larus marinus
  • Stercorarius parasiticus
  • Sterna hirundo
  • Sterna paradisaea
  • Sterna sandvicensis
  • Sternula albifrons
  • Arenaria interpres
  • Calidris alpina
  • Charadrius hiaticula
  • Haematopus ostralegus
  • Larus fuscus
  • Tadorna tadorna
  • Aythya fuligula
  • Bucephala clangula
  • Clangula hyemalis
  • Melanitta fusca
  • Anas platyrhynchos
  • Cygnus olor
  • Cepphus grylle
  • Mergellus albellus
  • Mergus merganser
  • Mergus serrator
  • Phalacrocorax carbo
  • Larus argentatus
  • Larus canus
  • Larus marinus
  • Larus ridibundus
  • Aythya fuligula
  • Bucephala clangula
  • Clangula hyemalis
  • Melanitta fusca
  • Anas platyrhynchos
  • Cygnus olor
  • Cepphus grylle
  • Mergellus albellus
  • Mergus merganser
  • Mergus serrator
  • Phalacrocorax carbo
  • Larus argentatus
  • Larus canus
  • Larus marinus
  • Larus ridibundus
  • Not Applicable
  • Haliaeetus albicilla
  • Not Applicable
  • Haliaeetus albicilla
  • Benthic-feeding birds (grouped)
  • Pelagic-feeding birds (grouped)
  • Surface-feeding birds (grouped)
  • Phocoena phocoena
  • Halichoerus grypus
  • Pusa hispida
  • Esox spp.
  • Perca fluviatilis
  • Sander lucioperca
  • Esox spp.
  • Perca fluviatilis
  • Sander lucioperca
  • Esox spp.
  • Perca fluviatilis
  • Sander lucioperca
  • Fish community
  • Fish community
  • Not Applicable
  • Alca torda
  • Uria aalge
  • Sterna paradisaea
  • Aythya ferina
  • Aythya fuligula
  • Bucephala clangula
  • Clangula hyemalis
  • Somateria mollissima
  • Anas acuta
  • Anas clypeata
  • Anas crecca
  • Anas penelope
  • Anas platyrhynchos
  • Anser anser
  • Branta canadensis
  • Fulica atra
  • Mergus merganser
  • Mergus serrator
  • Halichoerus grypus
  • Pusa hispida
GES criteria
D1C1
D1C2
D1C2
D1C2
D1C2
D1C2
D1C4
D1C4
D1C4
D1C4
D1C4
D1C2
D1C2
D1C2
D1C2
D1C4
D1C4
D1C4
D1C4
D1C2
D1C3
D4C4
D8C2
D1C1
D1C1
D1C1
D1C1
D1C1
D3C1
D3C2
D3C3
D4C1
D4C2
NotRelevan
D1C3
D1C3
NotRelevan
NotRelevan
NotRelevan
NotRelevan
Parameters
  • Mortality (weight/volume; number of individuals)
  • Abundance (number of individuals)
  • Abundance (number of individuals)
  • Abundance (number of individuals)
  • Abundance (number of individuals)
  • Abundance (number of individuals)
  • Distribution (range)
  • Distribution (range)
  • Distribution (range)
  • Distribution (range)
  • Distribution (range)
  • Abundance (number of individuals)
  • Abundance (number of individuals)
  • Abundance (number of individuals)
  • Abundance (number of individuals)
  • Distribution (range)
  • Distribution (range)
  • Distribution (range)
  • Distribution (range)
  • Abundance (number of individuals)
  • Breeding success
  • Brood size
  • Survival rate
  • Productivity
  • Extent
  • Mortality (weight/volume; number of individuals)
  • Mortality (weight/volume; number of individuals)
  • Mortality (weight/volume; number of individuals)
  • Mortality (weight/volume; number of individuals)
  • Mortality (weight/volume; number of individuals)
  • Mortality (weight/volume; number of individuals)
  • Biomass of Spawning Stock (SSB)
  • Size distribution
  • Other
  • Abundance (number of individuals)
  • Other
  • Other
  • Other
  • Mortality (weight/volume; number of individuals)
  • Mortality (weight/volume; number of individuals)
  • Mortality (weight/volume; number of individuals)
  • Mortality (weight/volume; number of individuals)
Parameter Other
age
age
Abundance of Cyprinidae
Abundance of Cyprinidae
Fishing effort (days)
Mortality
Mortality
Spatial scope
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • Terrestrial part of MS
  • EEZ (or similar)
  • Terrestrial part of MS
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
Marine reporting units
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS
  • BAL-FI-AS-COAST
  • BAL-FI-AS-OFFSHORE
  • BAL-FI-BB
  • BAL-FI-BB-COAST
  • BAL-FI-BS
  • BAL-FI-BS-COAST
  • BAL-FI-BS-OFFSHORE
  • BAL-FI-GF
  • BAL-FI-GF-COAST
  • BAL-FI-GF-OFFSHORE
  • BAL-FI-NB
  • BAL-FI-NB-OFFSHORE
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-QK-OFFSHORE
  • BAL-FI-AS
  • BAL-FI-AS-COAST
  • BAL-FI-AS-OFFSHORE
  • BAL-FI-BB
  • BAL-FI-BB-COAST
  • BAL-FI-BS
  • BAL-FI-BS-COAST
  • BAL-FI-BS-OFFSHORE
  • BAL-FI-GF
  • BAL-FI-GF-COAST
  • BAL-FI-GF-OFFSHORE
  • BAL-FI-NB
  • BAL-FI-NB-OFFSHORE
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-QK-OFFSHORE
  • BAL-FI-AS
  • BAL-FI-AS-COAST
  • BAL-FI-AS-OFFSHORE
  • BAL-FI-BB
  • BAL-FI-BB-COAST
  • BAL-FI-BS
  • BAL-FI-BS-COAST
  • BAL-FI-BS-OFFSHORE
  • BAL-FI-GF
  • BAL-FI-GF-COAST
  • BAL-FI-GF-OFFSHORE
  • BAL-FI-NB
  • BAL-FI-NB-OFFSHORE
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-QK-OFFSHORE
  • BAL-FI-AS
  • BAL-FI-AS-COAST
  • BAL-FI-AS-OFFSHORE
  • BAL-FI-BB
  • BAL-FI-BB-COAST
  • BAL-FI-BS
  • BAL-FI-BS-COAST
  • BAL-FI-BS-OFFSHORE
  • BAL-FI-GF
  • BAL-FI-GF-COAST
  • BAL-FI-GF-OFFSHORE
  • BAL-FI-NB
  • BAL-FI-NB-OFFSHORE
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-QK-OFFSHORE
  • BAL-FI-AS
  • BAL-FI-AS-COAST
  • BAL-FI-AS-OFFSHORE
  • BAL-FI-BB
  • BAL-FI-BB-COAST
  • BAL-FI-BS
  • BAL-FI-BS-COAST
  • BAL-FI-BS-OFFSHORE
  • BAL-FI-GF
  • BAL-FI-GF-COAST
  • BAL-FI-GF-OFFSHORE
  • BAL-FI-NB
  • BAL-FI-NB-OFFSHORE
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-QK-OFFSHORE
  • BAL-FI-AS
  • BAL-FI-AS-COAST
  • BAL-FI-AS-OFFSHORE
  • BAL-FI-BB
  • BAL-FI-BB-COAST
  • BAL-FI-BS
  • BAL-FI-BS-COAST
  • BAL-FI-BS-OFFSHORE
  • BAL-FI-GF
  • BAL-FI-GF-COAST
  • BAL-FI-GF-OFFSHORE
  • BAL-FI-NB
  • BAL-FI-NB-OFFSHORE
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-QK-OFFSHORE
  • BAL-FI-AS
  • BAL-FI-AS-COAST
  • BAL-FI-AS-OFFSHORE
  • BAL-FI-BB
  • BAL-FI-BB-COAST
  • BAL-FI-BS
  • BAL-FI-BS-COAST
  • BAL-FI-BS-OFFSHORE
  • BAL-FI-GF
  • BAL-FI-GF-COAST
  • BAL-FI-GF-OFFSHORE
  • BAL-FI-NB
  • BAL-FI-NB-OFFSHORE
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-QK-OFFSHORE
  • BAL-FI-AS
  • BAL-FI-AS-COAST
  • BAL-FI-AS-OFFSHORE
  • BAL-FI-BB
  • BAL-FI-BB-COAST
  • BAL-FI-BS
  • BAL-FI-BS-COAST
  • BAL-FI-BS-OFFSHORE
  • BAL-FI-GF
  • BAL-FI-GF-COAST
  • BAL-FI-GF-OFFSHORE
  • BAL-FI-NB
  • BAL-FI-NB-OFFSHORE
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-QK-OFFSHORE
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF-COAST
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF-COAST
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF-COAST
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF-COAST
  • BAL-FI-QK-COAST
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF-COAST
  • BAL-FI-GF-OFFSHORE
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF-COAST
  • BAL-FI-GF-OFFSHORE
  • BAL-FI-QK-COAST
  • BAL-FI
  • BAL-FI
  • BAL-FI
  • BAL-FI
Temporal scope (start date - end date)
1948-9999
1948-9999
1948-9999
1948-9999
1948-9999
1948-9999
1948-9999
1948-9999
1948-9999
1948-9999
1948-9999
1975-9999
1975-9999
1975-9999
1975-9999
1975-9999
1975-9999
1975-9999
1975-9999
1972-9999
1972-9999
1972-9999
1972-9999
1980-9999
1980-9999
1980-9999
1980-9999
1980-9999
1980-9999
1980-9999
1980-9999
1980-9999
1980-9999
1980-9999
1986-9999
1986-9999
1971-9999
1971-9999
1971-9999
1971-9999
Monitoring frequency
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Continually
Continually
Continually
Continually
Continually
Continually
Continually
Continually
Continually
Continually
Continually
Other
Other
Continually
Continually
Continually
Continually
Monitoring type
  • Visual observation
  • Visual observation
  • Visual observation
  • Visual observation
  • Visual observation
  • Visual observation
  • Visual observation
  • Visual observation
  • Visual observation
  • Visual observation
  • Visual observation
  • Remote flight imagery
  • Visual observation
  • Remote flight imagery
  • Visual observation
  • Remote flight imagery
  • Visual observation
  • Remote flight imagery
  • Visual observation
  • Remote flight imagery
  • Visual observation
  • Remote flight imagery
  • Visual observation
  • Remote flight imagery
  • Visual observation
  • Remote flight imagery
  • Visual observation
  • In-situ sampling land/beach
  • In-situ sampling land/beach
  • In-situ sampling land/beach
  • In-situ sampling land/beach
  • 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
  • Visual observation
  • In-situ sampling coastal
  • Visual observation
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
Monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
Monitoring method other
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Koskimies & Väisänen 1991, Hario et al. 1993 & 1995, Lehikoinen et al. 2017
Koskimies & Väisänen 1991, Hario et al. 1993 & 1995, Lehikoinen et al. 2017
Koskimies & Väisänen 1991, Hario et al. 1993 & 1995, Lehikoinen et al. 2017
Koskimies & Väisänen 1991, Hario et al. 1993 & 1995, Lehikoinen et al. 2017
Koskimies & Väisänen 1991, Hario et al. 1993 & 1995, Lehikoinen et al. 2017
Koskimies & Väisänen 1991, Hario et al. 1993 & 1995, Lehikoinen et al. 2017
Koskimies & Väisänen 1991, Hario et al. 1993 & 1995, Lehikoinen et al. 2017
Koskimies & Väisänen 1991, Hario et al. 1993 & 1995, Lehikoinen et al. 2017
https://helcom.fi/wp-content/uploads/2019/12/Birds-Marine-bird-health.pdf
https://helcom.fi/wp-content/uploads/2019/12/Birds-Marine-bird-health.pdf
https://helcom.fi/wp-content/uploads/2019/12/Birds-Marine-bird-health.pdf
https://helcom.fi/wp-content/uploads/2019/12/Birds-Marine-bird-health.pdf
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring is based on sightings of general public and ornithologists
Monitoring is based on sightings of general public and ornithologists
Hunting organizations carry out game questionnaires. Hunting statistics are maintained by the hunting organizations and stored into a database. Data on species requiring special permit is obtained through the licensing system.
Hunting organizations carry out game questionnaires. Hunting statistics are maintained by the hunting organizations and stored into a database. Data on species requiring special permit is obtained through the licensing system.
Hunting organizations carry out game questionnaires. Hunting statistics are maintained by the hunting organizations and stored into a database. Data on species requiring special permit is obtained through the licensing system.
Hunting organizations carry out game questionnaires. Hunting statistics are maintained by the hunting organizations and stored into a database. Data on species requiring special permit is obtained through the licensing system.
Quality control
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
Methods are according to Wetlands International- organizations standards. Methods described in HELCOM instructions (Helcom, 2015)
Methods are according to Wetlands International- organizations standards. Methods described in HELCOM instructions (Helcom, 2015)
Methods are according to Wetlands International- organizations standards. Methods described in HELCOM instructions (Helcom, 2015)
Methods are according to Wetlands International- organizations standards. Methods described in HELCOM instructions (Helcom, 2015)
Methods are according to Wetlands International- organizations standards. Methods described in HELCOM instructions (Helcom, 2015)
Methods are according to Wetlands International- organizations standards. Methods described in HELCOM instructions (Helcom, 2015)
Methods are according to Wetlands International- organizations standards. Methods described in HELCOM instructions (Helcom, 2015)
Methods are according to Wetlands International- organizations standards. Methods described in HELCOM instructions (Helcom, 2015)
Method developed in co-operation with Swedish and German authorities under HELCOM
Method developed in co-operation with Swedish and German authorities under HELCOM
Method developed in co-operation with Swedish and German authorities under HELCOM
Method developed in co-operation with Swedish and German authorities under HELCOM
Quality control - https://stat.luke.fi/en/commercial-marine-fishery
Quality control - https://stat.luke.fi/en/commercial-marine-fishery
Quality control - https://stat.luke.fi/en/commercial-marine-fishery
Quality control — https://stat.luke.fi/en/commercial-marine-fishery
Quality control - https://stat.luke.fi/en/commercial-marine-fishery
Quality control - https://stat.luke.fi/en/commercial-marine-fishery
Quality control - https://stat.luke.fi/en/commercial-marine-fishery
Quality control - https://stat.luke.fi/en/commercial-marine-fishery
Quality control — https://stat.luke.fi/en/commercial-marine-fishery
Quality control - https://stat.luke.fi/en/commercial-marine-fishery
Quality control - https://stat.luke.fi/en/commercial-marine-fishery
No specified quality control. Data comes from various sources, so mass mortalities are most likely reported
No specified quality control. Data comes from various sources, so mass mortalities are most likely reported
https://stat.luke.fi/tilasto/4428/laatuseloste/4697
https://stat.luke.fi/tilasto/4428/laatuseloste/4697
https://stat.luke.fi/tilasto/4428/laatuseloste/4697
https://stat.luke.fi/tilasto/4428/laatuseloste/4697
Data management
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Data stored in Finnish Museum of Natural History database. Data reported yearly to Wetlands Internationals database. HELCOM publishes indicator results yearly and publsihed indicator data.
Data stored in Finnish Museum of Natural History database. Data reported yearly to Wetlands Internationals database. HELCOM publishes indicator results yearly and publsihed indicator data.
Data stored in Finnish Museum of Natural History database. Data reported yearly to Wetlands Internationals database. HELCOM publishes indicator results yearly and publsihed indicator data.
Data stored in Finnish Museum of Natural History database. Data reported yearly to Wetlands Internationals database. HELCOM publishes indicator results yearly and publsihed indicator data.
Data stored in Finnish Museum of Natural History database. Data reported yearly to Wetlands Internationals database. HELCOM publishes indicator results yearly and publsihed indicator data.
Data stored in Finnish Museum of Natural History database. Data reported yearly to Wetlands Internationals database. HELCOM publishes indicator results yearly and publsihed indicator data.
Data stored in Finnish Museum of Natural History database. Data reported yearly to Wetlands Internationals database. HELCOM publishes indicator results yearly and publsihed indicator data.
Data stored in Finnish Museum of Natural History database. Data reported yearly to Wetlands Internationals database. HELCOM publishes indicator results yearly and publsihed indicator data.
Primary data stored in Finnish Museum of Natural History. HELCOM publishes indicator data.
Primary data stored in Finnish Museum of Natural History. HELCOM publishes indicator data.
Primary data stored in Finnish Museum of Natural History. HELCOM publishes indicator data.
Primary data stored in Finnish Museum of Natural History. HELCOM publishes indicator data.
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
Mortality data not publicly available Bird ringing data available online
Mortality data not publicly available Bird ringing data available online
Primary data only accessible for researchers
Primary data only accessible for researchers
Primary data only accessible for researchers
Primary data only accessible for researchers
Data access
Related indicator/name
Contact
References
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M., Lammi, E., Mikkola, M. & Södersved, J. 1993: Ovatko Ahvenanmaan vesilinnut "talvenkärkkyjiä" – kansainvälisten vesilintulaskentojen tuloksia vuosilta 1968-92. – Suomen Riista 39: 21– 32. Hario, M., Lammi, E., Mikkola, M., Södersved, J. 1995: January counts of waterfowl in SW Finland: the dependence on ice situation. – Ring 15 (1–2): 216 –222. HELCOM (2015), HELCOM guidelines for coordinated monitoring of wintering birds. 13 s. Koskimies & Väisänen (1991): Monitoring Bird Populations – A Manual of Methods Applied in Finland. – Zoological Museum, Finnish Museum of Natural History, University of Helsinki. Lehikoinen, A., Kuntze, K., Lehtiniemi, T. Mikkola-Roos, M. & Toivanen, T. 2017: Suomen keskitalven vesilintukantojen kannanarviot vuonna 2016 - muuttuva Suomi osana kansainvälistä seurantaa. - Linnut vuosikirja 2016:6-15.
Hario, M., Lammi, E., Mikkola, M. & Södersved, J. 1993: Ovatko Ahvenanmaan vesilinnut "talvenkärkkyjiä" – kansainvälisten vesilintulaskentojen tuloksia vuosilta 1968-92. – Suomen Riista 39: 21– 32. Hario, M., Lammi, E., Mikkola, M., Södersved, J. 1995: January counts of waterfowl in SW Finland: the dependence on ice situation. – Ring 15 (1–2): 216 –222. HELCOM (2015), HELCOM guidelines for coordinated monitoring of wintering birds. 13 s. Koskimies & Väisänen (1991): Monitoring Bird Populations – A Manual of Methods Applied in Finland. – Zoological Museum, Finnish Museum of Natural History, University of Helsinki. Lehikoinen, A., Kuntze, K., Lehtiniemi, T. Mikkola-Roos, M. & Toivanen, T. 2017: Suomen keskitalven vesilintukantojen kannanarviot vuonna 2016 - muuttuva Suomi osana kansainvälistä seurantaa. - Linnut vuosikirja 2016:6-15.
Hario, M., Lammi, E., Mikkola, M. & Södersved, J. 1993: Ovatko Ahvenanmaan vesilinnut "talvenkärkkyjiä" – kansainvälisten vesilintulaskentojen tuloksia vuosilta 1968-92. – Suomen Riista 39: 21– 32. Hario, M., Lammi, E., Mikkola, M., Södersved, J. 1995: January counts of waterfowl in SW Finland: the dependence on ice situation. – Ring 15 (1–2): 216 –222. HELCOM (2015), HELCOM guidelines for coordinated monitoring of wintering birds. 13 s. Koskimies & Väisänen (1991): Monitoring Bird Populations – A Manual of Methods Applied in Finland. – Zoological Museum, Finnish Museum of Natural History, University of Helsinki. Lehikoinen, A., Kuntze, K., Lehtiniemi, T. Mikkola-Roos, M. & Toivanen, T. 2017: Suomen keskitalven vesilintukantojen kannanarviot vuonna 2016 - muuttuva Suomi osana kansainvälistä seurantaa. - Linnut vuosikirja 2016:6-15.
Hario, M., Lammi, E., Mikkola, M. & Södersved, J. 1993: Ovatko Ahvenanmaan vesilinnut "talvenkärkkyjiä" – kansainvälisten vesilintulaskentojen tuloksia vuosilta 1968-92. – Suomen Riista 39: 21– 32. Hario, M., Lammi, E., Mikkola, M., Södersved, J. 1995: January counts of waterfowl in SW Finland: the dependence on ice situation. – Ring 15 (1–2): 216 –222. HELCOM (2015), HELCOM guidelines for coordinated monitoring of wintering birds. 13 s. Koskimies & Väisänen (1991): Monitoring Bird Populations – A Manual of Methods Applied in Finland. – Zoological Museum, Finnish Museum of Natural History, University of Helsinki. Lehikoinen, A., Kuntze, K., Lehtiniemi, T. Mikkola-Roos, M. & Toivanen, T. 2017: Suomen keskitalven vesilintukantojen kannanarviot vuonna 2016 - muuttuva Suomi osana kansainvälistä seurantaa. - Linnut vuosikirja 2016:6-15.
Hario, M., Lammi, E., Mikkola, M. & Södersved, J. 1993: Ovatko Ahvenanmaan vesilinnut "talvenkärkkyjiä" – kansainvälisten vesilintulaskentojen tuloksia vuosilta 1968-92. – Suomen Riista 39: 21– 32. Hario, M., Lammi, E., Mikkola, M., Södersved, J. 1995: January counts of waterfowl in SW Finland: the dependence on ice situation. – Ring 15 (1–2): 216 –222. HELCOM (2015), HELCOM guidelines for coordinated monitoring of wintering birds. 13 s. Koskimies & Väisänen (1991): Monitoring Bird Populations – A Manual of Methods Applied in Finland. – Zoological Museum, Finnish Museum of Natural History, University of Helsinki. Lehikoinen, A., Kuntze, K., Lehtiniemi, T. Mikkola-Roos, M. & Toivanen, T. 2017: Suomen keskitalven vesilintukantojen kannanarviot vuonna 2016 - muuttuva Suomi osana kansainvälistä seurantaa. - Linnut vuosikirja 2016:6-15.
Hario, M., Lammi, E., Mikkola, M. & Södersved, J. 1993: Ovatko Ahvenanmaan vesilinnut "talvenkärkkyjiä" – kansainvälisten vesilintulaskentojen tuloksia vuosilta 1968-92. – Suomen Riista 39: 21– 32. Hario, M., Lammi, E., Mikkola, M., Södersved, J. 1995: January counts of waterfowl in SW Finland: the dependence on ice situation. – Ring 15 (1–2): 216 –222. HELCOM (2015), HELCOM guidelines for coordinated monitoring of wintering birds. 13 s. Koskimies & Väisänen (1991): Monitoring Bird Populations – A Manual of Methods Applied in Finland. – Zoological Museum, Finnish Museum of Natural History, University of Helsinki. Lehikoinen, A., Kuntze, K., Lehtiniemi, T. Mikkola-Roos, M. & Toivanen, T. 2017: Suomen keskitalven vesilintukantojen kannanarviot vuonna 2016 - muuttuva Suomi osana kansainvälistä seurantaa. - Linnut vuosikirja 2016:6-15.
Hario, M., Lammi, E., Mikkola, M. & Södersved, J. 1993: Ovatko Ahvenanmaan vesilinnut "talvenkärkkyjiä" – kansainvälisten vesilintulaskentojen tuloksia vuosilta 1968-92. – Suomen Riista 39: 21– 32. Hario, M., Lammi, E., Mikkola, M., Södersved, J. 1995: January counts of waterfowl in SW Finland: the dependence on ice situation. – Ring 15 (1–2): 216 –222. HELCOM (2015), HELCOM guidelines for coordinated monitoring of wintering birds. 13 s. Koskimies & Väisänen (1991): Monitoring Bird Populations – A Manual of Methods Applied in Finland. – Zoological Museum, Finnish Museum of Natural History, University of Helsinki. Lehikoinen, A., Kuntze, K., Lehtiniemi, T. Mikkola-Roos, M. & Toivanen, T. 2017: Suomen keskitalven vesilintukantojen kannanarviot vuonna 2016 - muuttuva Suomi osana kansainvälistä seurantaa. - Linnut vuosikirja 2016:6-15.
Hario, M., Lammi, E., Mikkola, M. & Södersved, J. 1993: Ovatko Ahvenanmaan vesilinnut "talvenkärkkyjiä" – kansainvälisten vesilintulaskentojen tuloksia vuosilta 1968-92. – Suomen Riista 39: 21– 32. Hario, M., Lammi, E., Mikkola, M., Södersved, J. 1995: January counts of waterfowl in SW Finland: the dependence on ice situation. – Ring 15 (1–2): 216 –222. HELCOM (2015), HELCOM guidelines for coordinated monitoring of wintering birds. 13 s. Koskimies & Väisänen (1991): Monitoring Bird Populations – A Manual of Methods Applied in Finland. – Zoological Museum, Finnish Museum of Natural History, University of Helsinki. Lehikoinen, A., Kuntze, K., Lehtiniemi, T. Mikkola-Roos, M. & Toivanen, T. 2017: Suomen keskitalven vesilintukantojen kannanarviot vuonna 2016 - muuttuva Suomi osana kansainvälistä seurantaa. - Linnut vuosikirja 2016:6-15.
Stjernberg, T., Koivusaari, J., Högmander, J., Nuuja, I. & Lokki, H. 2011: Suomen merikotkat 2009 –2010. – Linnut-vuosikirja 2010: 18 –27. https://helcom.fi/media/core%20indicators/White-tailed-sea-eagle-productivity-HELCOM-core-indicator-2018.pdf
Stjernberg, T., Koivusaari, J., Högmander, J., Nuuja, I. & Lokki, H. 2011: Suomen merikotkat 2009 –2010. – Linnut-vuosikirja 2010: 18 –27. https://helcom.fi/media/core%20indicators/White-tailed-sea-eagle-productivity-HELCOM-core-indicator-2018.pdf
Stjernberg, T., Koivusaari, J., Högmander, J., Nuuja, I. & Lokki, H. 2011: Suomen merikotkat 2009 –2010. – Linnut-vuosikirja 2010: 18 –27. https://helcom.fi/media/core%20indicators/White-tailed-sea-eagle-productivity-HELCOM-core-indicator-2018.pdf
Stjernberg, T., Koivusaari, J., Högmander, J., Nuuja, I. & Lokki, H. 2011: Suomen merikotkat 2009 –2010. – Linnut-vuosikirja 2010: 18 –27. https://helcom.fi/media/core%20indicators/White-tailed-sea-eagle-productivity-HELCOM-core-indicator-2018.pdf
Hario, M., Hokkanen, T., Malkio, H. 1993. Itäisen Suomenlahden lintukuolemat. – Suomen Riista 39:7–20 Suleva, E. & Rintala, J. 2013. Ruokkilinnut Itämeren tilan indikaattoreina. Helsinki: RKTL:n työraportteja 1/2013. Riista- ja kalatalouden tutkimuslaitos. ISBN: 978-951-776-945-7. Mikkola-Roos, M. , Below, A., Lehikoinen, A & Rintala, J. 2018: Meriympäristön tila 2011-2016 : Merilinnut. Julk.: Korpinen, S., Laamanen, M., Suomela, J., Paavilainen, P., Lahtinen, T. & Ekebom, J. 2018. (toim.) Suomen meriympäristön tila 2018. Helsinki, Suomen ympäristökeskus. Ss. 198-207. SYKE:n julkaisuja 2018, 4. ISBN 978-952-11-4967-2 (nid.), 978-952-11-4968-9 (PDF), ISSN 2323-8895, (painettu), 2323-8909 (verkkojulkaisu). 2018: http://hdl.handle.net/10138/274086
Hario, M., Hokkanen, T., Malkio, H. 1993. Itäisen Suomenlahden lintukuolemat. – Suomen Riista 39:7–20 Suleva, E. & Rintala, J. 2013. Ruokkilinnut Itämeren tilan indikaattoreina. Helsinki: RKTL:n työraportteja 1/2013. Riista- ja kalatalouden tutkimuslaitos. ISBN: 978-951-776-945-7. Mikkola-Roos, M. , Below, A., Lehikoinen, A & Rintala, J. 2018: Meriympäristön tila 2011-2016 : Merilinnut. Julk.: Korpinen, S., Laamanen, M., Suomela, J., Paavilainen, P., Lahtinen, T. & Ekebom, J. 2018. (toim.) Suomen meriympäristön tila 2018. Helsinki, Suomen ympäristökeskus. Ss. 198-207. SYKE:n julkaisuja 2018, 4. ISBN 978-952-11-4967-2 (nid.), 978-952-11-4968-9 (PDF), ISSN 2323-8895, (painettu), 2323-8909 (verkkojulkaisu). 2018: http://hdl.handle.net/10138/274086