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.
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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.
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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 |
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|
|
|
|
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 |
|
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|
|
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 |
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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 |
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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 |
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Other policies and conventions |
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Regional cooperation - coordinating body |
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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 |
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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 |
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Monitoring details |
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â Live Yearbook 2010: 40-51
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Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â Live Yearbook 2010: 40-51
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Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â Live Yearbook 2010: 40-51
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Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â Live Yearbook 2010: 40-51
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Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â Live Yearbook 2010: 40-51
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Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â Live Yearbook 2010: 40-51
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Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â Live Yearbook 2010: 40-51
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Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â Live Yearbook 2010: 40-51
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Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â Live Yearbook 2010: 40-51
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Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â Live Yearbook 2010: 40-51
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Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â Live Yearbook 2010: 40-51
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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
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https://helcom.fi/wp-content/uploads/2019/12/Birds-Marine-bird-health.pdf
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https://helcom.fi/wp-content/uploads/2019/12/Birds-Marine-bird-health.pdf
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https://helcom.fi/wp-content/uploads/2019/12/Birds-Marine-bird-health.pdf
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Fishermensâ reporting to authorities.
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Fishermensâ reporting to authorities.
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Fishermensâ reporting to authorities.
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Fishermensâ reporting to authorities.
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Fishermensâ reporting to authorities.
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Fishermensâ reporting to authorities.
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Fishermensâ reporting to authorities.
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Fishermensâ reporting to authorities.
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Fishermensâ reporting to authorities.
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Fishermensâ reporting to authorities.
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Fishermensâ reporting to authorities.
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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, âpassiveâ monitoring, i.e. information obtained through other activities and monitoring.
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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, âpassiveâ monitoring, i.e. information obtained through other activities and monitoring.
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Features |
Grazing birds
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Benthic-feeding birds
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Grazing birds
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Pelagic-feeding birds
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Surface-feeding birds
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Wading birds
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Benthic-feeding birds
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Grazing birds
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Pelagic-feeding birds
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Surface-feeding birds
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Wading birds
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Benthic-feeding birds
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Grazing birds
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Pelagic-feeding birds
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Surface-feeding birds
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Benthic-feeding birds
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Grazing birds
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Pelagic-feeding birds
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Surface-feeding birds
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Disturbance of species (e.g. where they breed, rest and feed) due to human presence
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Surface-feeding birds
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Disturbance of species (e.g. where they breed, rest and feed) due to human presence
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Adverse effects on species or habitats
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Benthic-feeding birds
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Pelagic-feeding birds
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Surface-feeding birds
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Small toothed cetaceans
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Seals
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Commercially exploited fish and shellfish
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Commercially exploited fish and shellfish
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Commercially exploited fish and shellfish
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Coastal ecosystems
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Coastal ecosystems
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Fish and shellfish harvesting (professional, recreational)
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Pelagic-feeding birds
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Surface-feeding birds
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Benthic-feeding birds
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Grazing birds
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Pelagic-feeding birds
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Seals
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Elements |
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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 |
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Parameter Other |
age |
age |
Abundance of Cyprinidae |
Abundance of Cyprinidae |
Fishing effort (days) |
Mortality |
Mortality |
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Spatial scope |
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Marine reporting units |
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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 |
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Monitoring method |
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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 â 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 |
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Related indicator/name |
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Contact |
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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 |