Member State report / Art11 / 2020 / D1-B / Sweden / NE Atlantic: Greater North 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 Sweden
Region/subregion NE Atlantic: Greater North Sea
Reported by Swedish Agency for Marine and Water Management Gullbergs Strandgata 15, 411 04 Göteborg Box 11930,
Report date 2020-10-16
Report access

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Monitoring strategy description
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
The monitoring of seabirds provides a basis for assessing state primarily on the basis of abundance. The monitoring also allows a qualitative assessment of the distribution and health status of certain species. The monitoring of by-catches and hunting has the potential to provide a basis for direct impact, while other human activities and pressures that may affect seabirds, such as physical disturbance, fishing, shipping and hazardous substances, including oil spills, are included in other monitoring strategies. Large-scale changes in distributional range can be detected with current monitoring, although there is currently no indicator in place (criterion D1C4). The data collected in the monitoring of breeding seabirds will in the future be able to be used to assess the condition of the populations (D1C3), but there is no indicator in place yet. By using the monitoring of different human activities and pressures (e.g. shipping, constructions, fishing and oil spills) the aim is to be able to use these data together with data on mobile species to assess D1C5. JWGbird (Joint Ospar/Helcom/Ices Working Group on Marine Birds) are currently working on developing an indicator for D1C5. There are no targets in place specifically linked to marine birds, however, the targets for hazardous substances, eutrophication, marine litter, underwater noise and fishing activities are indirectly relevant to acheive good status also for birds. The related measures may cause positive changes in the marine bird populations, but just as for the targets the linkage between the human activities and pressures and how they may impact the populations are not always crystal clear.
Coverage of GES criteria
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Gaps and plans
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Wintering birds – The assessment of wintering seabirds is based entirely on data from land-based countings. The large numbers of birds that wintering in the archipelagos are thus poorly represented. JWGbird advocates that coordinated flight inventories of wintering seabirds should take place at intervals of a maximum of 6 years, which is something that will be fulfilled at least in the short term with the flight inventories to be carried out during the winter of 2020. JWGbird is currently working on developing methods to assess wintering birds at sea according to D1C2. Breeding birds – Knowledge of reproductive success over time would serve as an effective "early warning system" and would provide a basis for D1C3 (population condition). Within the monitoring of breeding coastal birds, reproduction data is collected for eider, but within a pilot inventory also for other species. Consideration should be given to including the pilot inventory in the continuously funded monitoring. Unused in this context is high-quality data collected outside the national environmental monitoring. Sweden will investigate what such data exists and their availability. Bycatch – Monitoring is being improved thanks to a number of ongoing projects in the Baltic Sea, the Sound, Kattegat and Skagerrak. These projects are complementing the regular monitoring of commersial fisheries discards, where bycaught birds are noted by human observers onboard, but where numbers are too low to enable a confident assessment of D1C1. Cameras onboard are therefore being tested as a complement to the observers.
Related targets
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
  • ANSSE-A.1_Tillförsel_näringsämnen
  • ANSSE-B.2_Tillförsel_farliga_ämnen_effekt
  • ANSSE-E.1_Skräp
  • BALSE-A.1_Tillförsel_näringsämnen
  • BALSE-B.2_Tillförsel_farliga_ämnen_effekt
  • BALSE-E.1_Skräp
Coverage of targets
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Related measures
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
  • ANSSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • ANSSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • ANSSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • ANSSE-M037 - 'Species Protection Ordinance 2007: 845'
  • BALSE-M007 - 'ÅPH 7 – Investigate and establish additional fishing area closures'
  • BALSE-M008 - 'ÅPH 8 – Investigate general fishing closures for coastal species'
  • BALSE-M009 - 'ÅPH 9 – Adjust fleet capacity in line with fishing opportunities'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • BALSE-M037 - 'Species Protection Ordinance 2007: 845'
Coverage of measures
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Adequate monitoring is in place by July 2020
Related monitoring programmes
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
  • SE-D1-hunting
  • SE-D1D3-bycatch
  • SE-D1D4-seabirds
Programme code
SE-D1-hunting
SE-D1-hunting
SE-D1D3-bycatch
SE-D1D3-bycatch
SE-D1D4-seabirds
SE-D1D4-seabirds
SE-D1D4-seabirds
SE-D1D4-seabirds
SE-D1D4-seabirds
SE-D1D4-seabirds
SE-D1D4-seabirds
SE-D1D4-seabirds
SE-D1D4-seabirds
SE-D1D4-seabirds
SE-D1D4-seabirds
SE-D1D4-seabirds
SE-D1D4-seabirds
SE-D1D4-seabirds
SE-D1D4-seabirds
SE-D1D4-seabirds
SE-D1D4-seabirds
SE-D1D4-seabirds
SE-D1D4-seabirds
SE-D1D4-seabirds
SE-D1D4-seabirds
Programme name
Hunting of birds and seals
Hunting of birds and seals
Bycatch
Bycatch
Seabirds
Seabirds
Seabirds
Seabirds
Seabirds
Seabirds
Seabirds
Seabirds
Seabirds
Seabirds
Seabirds
Seabirds
Seabirds
Seabirds
Seabirds
Seabirds
Seabirds
Seabirds
Seabirds
Seabirds
Seabirds
Update type
New programme
New programme
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
Old programme codes
  • ANSSE-COMFISH-D3-Utkast
  • BALSE-COMFISH-D3-Utkast
  • ANSSE-COMFISH-D3-Utkast
  • BALSE-COMFISH-D3-Utkast
  • ANSSE-Birds-D14-Overvintrande
  • BALSE-Birds-D14-Hackande
  • BALSE-Birds-D14-Overvintrande
  • ANSSE-Birds-D14-Overvintrande
  • BALSE-Birds-D14-Hackande
  • BALSE-Birds-D14-Overvintrande
  • ANSSE-Birds-D14-Overvintrande
  • BALSE-Birds-D14-Hackande
  • BALSE-Birds-D14-Overvintrande
  • ANSSE-Birds-D14-Overvintrande
  • BALSE-Birds-D14-Hackande
  • BALSE-Birds-D14-Overvintrande
  • ANSSE-Birds-D14-Overvintrande
  • BALSE-Birds-D14-Hackande
  • BALSE-Birds-D14-Overvintrande
  • ANSSE-Birds-D14-Overvintrande
  • BALSE-Birds-D14-Hackande
  • BALSE-Birds-D14-Overvintrande
  • ANSSE-Birds-D14-Overvintrande
  • BALSE-Birds-D14-Hackande
  • BALSE-Birds-D14-Overvintrande
  • ANSSE-Birds-D14-Overvintrande
  • BALSE-Birds-D14-Hackande
  • BALSE-Birds-D14-Overvintrande
  • ANSSE-Birds-D14-Overvintrande
  • BALSE-Birds-D14-Hackande
  • BALSE-Birds-D14-Overvintrande
  • ANSSE-Birds-D14-Overvintrande
  • BALSE-Birds-D14-Hackande
  • BALSE-Birds-D14-Overvintrande
  • ANSSE-Birds-D14-Overvintrande
  • BALSE-Birds-D14-Hackande
  • BALSE-Birds-D14-Overvintrande
  • ANSSE-Birds-D14-Overvintrande
  • BALSE-Birds-D14-Hackande
  • BALSE-Birds-D14-Overvintrande
  • ANSSE-Birds-D14-Overvintrande
  • BALSE-Birds-D14-Hackande
  • BALSE-Birds-D14-Overvintrande
  • ANSSE-Birds-D14-Overvintrande
  • BALSE-Birds-D14-Hackande
  • BALSE-Birds-D14-Overvintrande
  • ANSSE-Birds-D14-Overvintrande
  • BALSE-Birds-D14-Hackande
  • BALSE-Birds-D14-Overvintrande
  • ANSSE-Birds-D14-Overvintrande
  • BALSE-Birds-D14-Hackande
  • BALSE-Birds-D14-Overvintrande
  • ANSSE-Birds-D14-Overvintrande
  • BALSE-Birds-D14-Hackande
  • BALSE-Birds-D14-Overvintrande
  • ANSSE-Birds-D14-Overvintrande
  • BALSE-Birds-D14-Hackande
  • BALSE-Birds-D14-Overvintrande
  • ANSSE-Birds-D14-Overvintrande
  • BALSE-Birds-D14-Hackande
  • BALSE-Birds-D14-Overvintrande
  • ANSSE-Birds-D14-Overvintrande
  • BALSE-Birds-D14-Hackande
  • BALSE-Birds-D14-Overvintrande
  • ANSSE-Birds-D14-Overvintrande
  • BALSE-Birds-D14-Hackande
  • BALSE-Birds-D14-Overvintrande
Programme description
In Sweden, hunting for seals and certain species of seabirds is regulated by the Hunting Act, the Hunting Ordinance and various supplementary regulations as well as other legally binding documents. The hunt can be carried out either as predator control, license hunting or general hunting. The different types of hunting have partly different purposes and conditions linked to the conduct of the hunt. The main purpose of the predator control is to limit the damage that wildlife causes to human activities and interests and in some cases the damage that a species causes to other animals and plants. In license hunting, the kills and thus the development of the game stock in question must be adapted to the availability of game and with regard to public and private interests. The hunt must also have a clear purpose, e.g. to prevent the damage caused by wildlife. In the case of general hunting, the hunting right holder has the opportunity to hunt an unlimited number of animals of the permitted type during the permitted hunting period, however, the hunting must be adapted to the availability of game. Predator control and license hunting is conducted following a decision by an authority. General hunting seasons are regulated in the Hunting Ordinance. The Hunting Ordinance also contains provisions that certain species may be hunted on the hunters own initiative to prevent the damage caused by wildlife. Historically, intensive hunting has been a contributing factor to some species being endangered, but today hunting is regulated so that it does not cause a negative impact on the viability of stocks. Hunting, however, is one of several human activities that must be monitored in order to be able to follow the development of different populations of birds and seals.
In Sweden, hunting for seals and certain species of seabirds is regulated by the Hunting Act, the Hunting Ordinance and various supplementary regulations as well as other legally binding documents. The hunt can be carried out either as predator control, license hunting or general hunting. The different types of hunting have partly different purposes and conditions linked to the conduct of the hunt. The main purpose of the predator control is to limit the damage that wildlife causes to human activities and interests and in some cases the damage that a species causes to other animals and plants. In license hunting, the kills and thus the development of the game stock in question must be adapted to the availability of game and with regard to public and private interests. The hunt must also have a clear purpose, e.g. to prevent the damage caused by wildlife. In the case of general hunting, the hunting right holder has the opportunity to hunt an unlimited number of animals of the permitted type during the permitted hunting period, however, the hunting must be adapted to the availability of game. Predator control and license hunting is conducted following a decision by an authority. General hunting seasons are regulated in the Hunting Ordinance. The Hunting Ordinance also contains provisions that certain species may be hunted on the hunters own initiative to prevent the damage caused by wildlife. Historically, intensive hunting has been a contributing factor to some species being endangered, but today hunting is regulated so that it does not cause a negative impact on the viability of stocks. Hunting, however, is one of several human activities that must be monitored in order to be able to follow the development of different populations of birds and seals.
In the regular sampling carried out on board commercial fishing vessels in accordance with EU data collection regulations ((EU) 2017/1004, (EU) 2016/1251), as well as the regulation on the conservation of fishery resources and the protection of marine ecosystems (EU ) 2019/1241, information regarding by-catch is obtained. All fish species, commercial shellfish, mammals and birds are noted. Sampling takes place mainly on vessels fishing with various bottom trawls. Data collection carried out according to the EU data collection regulations is coordinated internationally between Member States in regional data collection coordination groups. Sweden participates in two such groups RCG Baltic and RCG North Sea and Eastern Arctic (to which the Skagerrak and Kattegat belong). Furthermore, a lot of international coordination and development work is done within ICES´s various expert groups (for by-catches mainly WGBYC). Sweden participates actively in these groups. Pilot studies were carried out in 2017-2019 with the aim of conducting by-catch sampling in 2020 in fisheries that use passive gear (nets and hooks). The purpose is to increase knowledge about by-catches in these fisheries, to test whether it is possible to estimate by-catches by having observers on board fishing boats, and if this is an effective method. Sampling of nets in the Sound and in the Kattegat will be included in the regular sampling from 2020. However, no ongoing monitoring of passive gear is currently planned in the Baltic Proper as previous pilots observed fewer by-catches there. So based on risk, monitoring in the Sound and Kattegatt are therefore prioritized. The Skagerrak could possibly be added after the pilot study there is completed in 2021. The pilot studies have shown that it also works to monitor the fish with passive gear with the help of observers (the challenge is that the vessels are small). However, the question remains whether this is the most effective way of estimating the total amount of by-catches in the fisheries. The problem is that observers can only cover a small part of the total fishing effort and that by-catches of many species (such as harbour porpoises and various birds) are relatively uncommon. This means that there will be few observations and thus uncertainty in the estimates of the total amount of by-catches. In 2020, therefore, a new pilot project was initiated where surveillance with the help of cameras is tested and compared with surveillance with the help
In the regular sampling carried out on board commercial fishing vessels in accordance with EU data collection regulations ((EU) 2017/1004, (EU) 2016/1251), as well as the regulation on the conservation of fishery resources and the protection of marine ecosystems (EU ) 2019/1241, information regarding by-catch is obtained. All fish species, commercial shellfish, mammals and birds are noted. Sampling takes place mainly on vessels fishing with various bottom trawls. Data collection carried out according to the EU data collection regulations is coordinated internationally between Member States in regional data collection coordination groups. Sweden participates in two such groups RCG Baltic and RCG North Sea and Eastern Arctic (to which the Skagerrak and Kattegat belong). Furthermore, a lot of international coordination and development work is done within ICES´s various expert groups (for by-catches mainly WGBYC). Sweden participates actively in these groups. Pilot studies were carried out in 2017-2019 with the aim of conducting by-catch sampling in 2020 in fisheries that use passive gear (nets and hooks). The purpose is to increase knowledge about by-catches in these fisheries, to test whether it is possible to estimate by-catches by having observers on board fishing boats, and if this is an effective method. Sampling of nets in the Sound and in the Kattegat will be included in the regular sampling from 2020. However, no ongoing monitoring of passive gear is currently planned in the Baltic Proper as previous pilots observed fewer by-catches there. So based on risk, monitoring in the Sound and Kattegatt are therefore prioritized. The Skagerrak could possibly be added after the pilot study there is completed in 2021. The pilot studies have shown that it also works to monitor the fish with passive gear with the help of observers (the challenge is that the vessels are small). However, the question remains whether this is the most effective way of estimating the total amount of by-catches in the fisheries. The problem is that observers can only cover a small part of the total fishing effort and that by-catches of many species (such as harbour porpoises and various birds) are relatively uncommon. This means that there will be few observations and thus uncertainty in the estimates of the total amount of by-catches. In 2020, therefore, a new pilot project was initiated where surveillance with the help of cameras is tested and compared with surveillance with the help
Seabirds are an important part of the marine ecosystem, as most species are high up in the food chain. The monitoring of breeding and wintering birds along the coast and in the offshore areas aims to follow the population development over time, which can be affected by changing conditions in the food web but also by the direct impact that arises from a number of different human activities. The status of seabirds therefore gives a general indication of the state of the ecosystem and corresponds to the cumulative impact of different pressures. Breeding and wintering birds are nationally monitored annually along the Swedish coast. Standardized inventories of wintering birds along the coast of Sweden have been ongoing annually since 1967 and are coordinated internationally within the International Waterbird Census. Breeding birds have been monitored on a large scale since 2010. At the local level, monitoring of breeding coastal birds is also carried out in a number of coastal counties, where several of the programmes are linked to the national programme. With an approximate six-year interval, inventories of wintering seabird species in the offshore areas are carried out, in order to supplement the annual inventories. These inventories are coordinated internationally and were first carried out in 1992-93. In 2020, inventories will be carried out in the offshore sea areas within the HELCOM and OSPAR regions in order to improve knowledge of the species that live there, especially hareld (Clangula hyemalis). The inventories are coordinated with other countries around the Baltic Sea and the North Sea through the working group JWGbird. Somateria mollissima (Anas molissima) is also monitored, but was not in the element list
Seabirds are an important part of the marine ecosystem, as most species are high up in the food chain. The monitoring of breeding and wintering birds along the coast and in the offshore areas aims to follow the population development over time, which can be affected by changing conditions in the food web but also by the direct impact that arises from a number of different human activities. The status of seabirds therefore gives a general indication of the state of the ecosystem and corresponds to the cumulative impact of different pressures. Breeding and wintering birds are nationally monitored annually along the Swedish coast. Standardized inventories of wintering birds along the coast of Sweden have been ongoing annually since 1967 and are coordinated internationally within the International Waterbird Census. Breeding birds have been monitored on a large scale since 2010. At the local level, monitoring of breeding coastal birds is also carried out in a number of coastal counties, where several of the programmes are linked to the national programme. With an approximate six-year interval, inventories of wintering seabird species in the offshore areas are carried out, in order to supplement the annual inventories. These inventories are coordinated internationally and were first carried out in 1992-93. In 2020, inventories will be carried out in the offshore sea areas within the HELCOM and OSPAR regions in order to improve knowledge of the species that live there, especially hareld (Clangula hyemalis). The inventories are coordinated with other countries around the Baltic Sea and the North Sea through the working group JWGbird. Somateria mollissima (Anas molissima) is also monitored, but was not in the element list
Seabirds are an important part of the marine ecosystem, as most species are high up in the food chain. The monitoring of breeding and wintering birds along the coast and in the offshore areas aims to follow the population development over time, which can be affected by changing conditions in the food web but also by the direct impact that arises from a number of different human activities. The status of seabirds therefore gives a general indication of the state of the ecosystem and corresponds to the cumulative impact of different pressures. Breeding and wintering birds are nationally monitored annually along the Swedish coast. Standardized inventories of wintering birds along the coast of Sweden have been ongoing annually since 1967 and are coordinated internationally within the International Waterbird Census. Breeding birds have been monitored on a large scale since 2010. At the local level, monitoring of breeding coastal birds is also carried out in a number of coastal counties, where several of the programmes are linked to the national programme. With an approximate six-year interval, inventories of wintering seabird species in the offshore areas are carried out, in order to supplement the annual inventories. These inventories are coordinated internationally and were first carried out in 1992-93. In 2020, inventories will be carried out in the offshore sea areas within the HELCOM and OSPAR regions in order to improve knowledge of the species that live there, especially hareld (Clangula hyemalis). The inventories are coordinated with other countries around the Baltic Sea and the North Sea through the working group JWGbird. Somateria mollissima (Anas molissima) is also monitored, but was not in the element list
Seabirds are an important part of the marine ecosystem, as most species are high up in the food chain. The monitoring of breeding and wintering birds along the coast and in the offshore areas aims to follow the population development over time, which can be affected by changing conditions in the food web but also by the direct impact that arises from a number of different human activities. The status of seabirds therefore gives a general indication of the state of the ecosystem and corresponds to the cumulative impact of different pressures. Breeding and wintering birds are nationally monitored annually along the Swedish coast. Standardized inventories of wintering birds along the coast of Sweden have been ongoing annually since 1967 and are coordinated internationally within the International Waterbird Census. Breeding birds have been monitored on a large scale since 2010. At the local level, monitoring of breeding coastal birds is also carried out in a number of coastal counties, where several of the programmes are linked to the national programme. With an approximate six-year interval, inventories of wintering seabird species in the offshore areas are carried out, in order to supplement the annual inventories. These inventories are coordinated internationally and were first carried out in 1992-93. In 2020, inventories will be carried out in the offshore sea areas within the HELCOM and OSPAR regions in order to improve knowledge of the species that live there, especially hareld (Clangula hyemalis). The inventories are coordinated with other countries around the Baltic Sea and the North Sea through the working group JWGbird. Somateria mollissima (Anas molissima) is also monitored, but was not in the element list
Seabirds are an important part of the marine ecosystem, as most species are high up in the food chain. The monitoring of breeding and wintering birds along the coast and in the offshore areas aims to follow the population development over time, which can be affected by changing conditions in the food web but also by the direct impact that arises from a number of different human activities. The status of seabirds therefore gives a general indication of the state of the ecosystem and corresponds to the cumulative impact of different pressures. Breeding and wintering birds are nationally monitored annually along the Swedish coast. Standardized inventories of wintering birds along the coast of Sweden have been ongoing annually since 1967 and are coordinated internationally within the International Waterbird Census. Breeding birds have been monitored on a large scale since 2010. At the local level, monitoring of breeding coastal birds is also carried out in a number of coastal counties, where several of the programmes are linked to the national programme. With an approximate six-year interval, inventories of wintering seabird species in the offshore areas are carried out, in order to supplement the annual inventories. These inventories are coordinated internationally and were first carried out in 1992-93. In 2020, inventories will be carried out in the offshore sea areas within the HELCOM and OSPAR regions in order to improve knowledge of the species that live there, especially hareld (Clangula hyemalis). The inventories are coordinated with other countries around the Baltic Sea and the North Sea through the working group JWGbird. Somateria mollissima (Anas molissima) is also monitored, but was not in the element list
Seabirds are an important part of the marine ecosystem, as most species are high up in the food chain. The monitoring of breeding and wintering birds along the coast and in the offshore areas aims to follow the population development over time, which can be affected by changing conditions in the food web but also by the direct impact that arises from a number of different human activities. The status of seabirds therefore gives a general indication of the state of the ecosystem and corresponds to the cumulative impact of different pressures. Breeding and wintering birds are nationally monitored annually along the Swedish coast. Standardized inventories of wintering birds along the coast of Sweden have been ongoing annually since 1967 and are coordinated internationally within the International Waterbird Census. Breeding birds have been monitored on a large scale since 2010. At the local level, monitoring of breeding coastal birds is also carried out in a number of coastal counties, where several of the programmes are linked to the national programme. With an approximate six-year interval, inventories of wintering seabird species in the offshore areas are carried out, in order to supplement the annual inventories. These inventories are coordinated internationally and were first carried out in 1992-93. In 2020, inventories will be carried out in the offshore sea areas within the HELCOM and OSPAR regions in order to improve knowledge of the species that live there, especially hareld (Clangula hyemalis). The inventories are coordinated with other countries around the Baltic Sea and the North Sea through the working group JWGbird. Somateria mollissima (Anas molissima) is also monitored, but was not in the element list
Seabirds are an important part of the marine ecosystem, as most species are high up in the food chain. The monitoring of breeding and wintering birds along the coast and in the offshore areas aims to follow the population development over time, which can be affected by changing conditions in the food web but also by the direct impact that arises from a number of different human activities. The status of seabirds therefore gives a general indication of the state of the ecosystem and corresponds to the cumulative impact of different pressures. Breeding and wintering birds are nationally monitored annually along the Swedish coast. Standardized inventories of wintering birds along the coast of Sweden have been ongoing annually since 1967 and are coordinated internationally within the International Waterbird Census. Breeding birds have been monitored on a large scale since 2010. At the local level, monitoring of breeding coastal birds is also carried out in a number of coastal counties, where several of the programmes are linked to the national programme. With an approximate six-year interval, inventories of wintering seabird species in the offshore areas are carried out, in order to supplement the annual inventories. These inventories are coordinated internationally and were first carried out in 1992-93. In 2020, inventories will be carried out in the offshore sea areas within the HELCOM and OSPAR regions in order to improve knowledge of the species that live there, especially hareld (Clangula hyemalis). The inventories are coordinated with other countries around the Baltic Sea and the North Sea through the working group JWGbird. Somateria mollissima (Anas molissima) is also monitored, but was not in the element list
Seabirds are an important part of the marine ecosystem, as most species are high up in the food chain. The monitoring of breeding and wintering birds along the coast and in the offshore areas aims to follow the population development over time, which can be affected by changing conditions in the food web but also by the direct impact that arises from a number of different human activities. The status of seabirds therefore gives a general indication of the state of the ecosystem and corresponds to the cumulative impact of different pressures. Breeding and wintering birds are nationally monitored annually along the Swedish coast. Standardized inventories of wintering birds along the coast of Sweden have been ongoing annually since 1967 and are coordinated internationally within the International Waterbird Census. Breeding birds have been monitored on a large scale since 2010. At the local level, monitoring of breeding coastal birds is also carried out in a number of coastal counties, where several of the programmes are linked to the national programme. With an approximate six-year interval, inventories of wintering seabird species in the offshore areas are carried out, in order to supplement the annual inventories. These inventories are coordinated internationally and were first carried out in 1992-93. In 2020, inventories will be carried out in the offshore sea areas within the HELCOM and OSPAR regions in order to improve knowledge of the species that live there, especially hareld (Clangula hyemalis). The inventories are coordinated with other countries around the Baltic Sea and the North Sea through the working group JWGbird. Somateria mollissima (Anas molissima) is also monitored, but was not in the element list
Seabirds are an important part of the marine ecosystem, as most species are high up in the food chain. The monitoring of breeding and wintering birds along the coast and in the offshore areas aims to follow the population development over time, which can be affected by changing conditions in the food web but also by the direct impact that arises from a number of different human activities. The status of seabirds therefore gives a general indication of the state of the ecosystem and corresponds to the cumulative impact of different pressures. Breeding and wintering birds are nationally monitored annually along the Swedish coast. Standardized inventories of wintering birds along the coast of Sweden have been ongoing annually since 1967 and are coordinated internationally within the International Waterbird Census. Breeding birds have been monitored on a large scale since 2010. At the local level, monitoring of breeding coastal birds is also carried out in a number of coastal counties, where several of the programmes are linked to the national programme. With an approximate six-year interval, inventories of wintering seabird species in the offshore areas are carried out, in order to supplement the annual inventories. These inventories are coordinated internationally and were first carried out in 1992-93. In 2020, inventories will be carried out in the offshore sea areas within the HELCOM and OSPAR regions in order to improve knowledge of the species that live there, especially hareld (Clangula hyemalis). The inventories are coordinated with other countries around the Baltic Sea and the North Sea through the working group JWGbird. Somateria mollissima (Anas molissima) is also monitored, but was not in the element list
Seabirds are an important part of the marine ecosystem, as most species are high up in the food chain. The monitoring of breeding and wintering birds along the coast and in the offshore areas aims to follow the population development over time, which can be affected by changing conditions in the food web but also by the direct impact that arises from a number of different human activities. The status of seabirds therefore gives a general indication of the state of the ecosystem and corresponds to the cumulative impact of different pressures. Breeding and wintering birds are nationally monitored annually along the Swedish coast. Standardized inventories of wintering birds along the coast of Sweden have been ongoing annually since 1967 and are coordinated internationally within the International Waterbird Census. Breeding birds have been monitored on a large scale since 2010. At the local level, monitoring of breeding coastal birds is also carried out in a number of coastal counties, where several of the programmes are linked to the national programme. With an approximate six-year interval, inventories of wintering seabird species in the offshore areas are carried out, in order to supplement the annual inventories. These inventories are coordinated internationally and were first carried out in 1992-93. In 2020, inventories will be carried out in the offshore sea areas within the HELCOM and OSPAR regions in order to improve knowledge of the species that live there, especially hareld (Clangula hyemalis). The inventories are coordinated with other countries around the Baltic Sea and the North Sea through the working group JWGbird. Somateria mollissima (Anas molissima) is also monitored, but was not in the element list
Seabirds are an important part of the marine ecosystem, as most species are high up in the food chain. The monitoring of breeding and wintering birds along the coast and in the offshore areas aims to follow the population development over time, which can be affected by changing conditions in the food web but also by the direct impact that arises from a number of different human activities. The status of seabirds therefore gives a general indication of the state of the ecosystem and corresponds to the cumulative impact of different pressures. Breeding and wintering birds are nationally monitored annually along the Swedish coast. Standardized inventories of wintering birds along the coast of Sweden have been ongoing annually since 1967 and are coordinated internationally within the International Waterbird Census. Breeding birds have been monitored on a large scale since 2010. At the local level, monitoring of breeding coastal birds is also carried out in a number of coastal counties, where several of the programmes are linked to the national programme. With an approximate six-year interval, inventories of wintering seabird species in the offshore areas are carried out, in order to supplement the annual inventories. These inventories are coordinated internationally and were first carried out in 1992-93. In 2020, inventories will be carried out in the offshore sea areas within the HELCOM and OSPAR regions in order to improve knowledge of the species that live there, especially hareld (Clangula hyemalis). The inventories are coordinated with other countries around the Baltic Sea and the North Sea through the working group JWGbird. Somateria mollissima (Anas molissima) is also monitored, but was not in the element list
Seabirds are an important part of the marine ecosystem, as most species are high up in the food chain. The monitoring of breeding and wintering birds along the coast and in the offshore areas aims to follow the population development over time, which can be affected by changing conditions in the food web but also by the direct impact that arises from a number of different human activities. The status of seabirds therefore gives a general indication of the state of the ecosystem and corresponds to the cumulative impact of different pressures. Breeding and wintering birds are nationally monitored annually along the Swedish coast. Standardized inventories of wintering birds along the coast of Sweden have been ongoing annually since 1967 and are coordinated internationally within the International Waterbird Census. Breeding birds have been monitored on a large scale since 2010. At the local level, monitoring of breeding coastal birds is also carried out in a number of coastal counties, where several of the programmes are linked to the national programme. With an approximate six-year interval, inventories of wintering seabird species in the offshore areas are carried out, in order to supplement the annual inventories. These inventories are coordinated internationally and were first carried out in 1992-93. In 2020, inventories will be carried out in the offshore sea areas within the HELCOM and OSPAR regions in order to improve knowledge of the species that live there, especially hareld (Clangula hyemalis). The inventories are coordinated with other countries around the Baltic Sea and the North Sea through the working group JWGbird. Somateria mollissima (Anas molissima) is also monitored, but was not in the element list
Seabirds are an important part of the marine ecosystem, as most species are high up in the food chain. The monitoring of breeding and wintering birds along the coast and in the offshore areas aims to follow the population development over time, which can be affected by changing conditions in the food web but also by the direct impact that arises from a number of different human activities. The status of seabirds therefore gives a general indication of the state of the ecosystem and corresponds to the cumulative impact of different pressures. Breeding and wintering birds are nationally monitored annually along the Swedish coast. Standardized inventories of wintering birds along the coast of Sweden have been ongoing annually since 1967 and are coordinated internationally within the International Waterbird Census. Breeding birds have been monitored on a large scale since 2010. At the local level, monitoring of breeding coastal birds is also carried out in a number of coastal counties, where several of the programmes are linked to the national programme. With an approximate six-year interval, inventories of wintering seabird species in the offshore areas are carried out, in order to supplement the annual inventories. These inventories are coordinated internationally and were first carried out in 1992-93. In 2020, inventories will be carried out in the offshore sea areas within the HELCOM and OSPAR regions in order to improve knowledge of the species that live there, especially hareld (Clangula hyemalis). The inventories are coordinated with other countries around the Baltic Sea and the North Sea through the working group JWGbird. Somateria mollissima (Anas molissima) is also monitored, but was not in the element list
Seabirds are an important part of the marine ecosystem, as most species are high up in the food chain. The monitoring of breeding and wintering birds along the coast and in the offshore areas aims to follow the population development over time, which can be affected by changing conditions in the food web but also by the direct impact that arises from a number of different human activities. The status of seabirds therefore gives a general indication of the state of the ecosystem and corresponds to the cumulative impact of different pressures. Breeding and wintering birds are nationally monitored annually along the Swedish coast. Standardized inventories of wintering birds along the coast of Sweden have been ongoing annually since 1967 and are coordinated internationally within the International Waterbird Census. Breeding birds have been monitored on a large scale since 2010. At the local level, monitoring of breeding coastal birds is also carried out in a number of coastal counties, where several of the programmes are linked to the national programme. With an approximate six-year interval, inventories of wintering seabird species in the offshore areas are carried out, in order to supplement the annual inventories. These inventories are coordinated internationally and were first carried out in 1992-93. In 2020, inventories will be carried out in the offshore sea areas within the HELCOM and OSPAR regions in order to improve knowledge of the species that live there, especially hareld (Clangula hyemalis). The inventories are coordinated with other countries around the Baltic Sea and the North Sea through the working group JWGbird. Somateria mollissima (Anas molissima) is also monitored, but was not in the element list
Seabirds are an important part of the marine ecosystem, as most species are high up in the food chain. The monitoring of breeding and wintering birds along the coast and in the offshore areas aims to follow the population development over time, which can be affected by changing conditions in the food web but also by the direct impact that arises from a number of different human activities. The status of seabirds therefore gives a general indication of the state of the ecosystem and corresponds to the cumulative impact of different pressures. Breeding and wintering birds are nationally monitored annually along the Swedish coast. Standardized inventories of wintering birds along the coast of Sweden have been ongoing annually since 1967 and are coordinated internationally within the International Waterbird Census. Breeding birds have been monitored on a large scale since 2010. At the local level, monitoring of breeding coastal birds is also carried out in a number of coastal counties, where several of the programmes are linked to the national programme. With an approximate six-year interval, inventories of wintering seabird species in the offshore areas are carried out, in order to supplement the annual inventories. These inventories are coordinated internationally and were first carried out in 1992-93. In 2020, inventories will be carried out in the offshore sea areas within the HELCOM and OSPAR regions in order to improve knowledge of the species that live there, especially hareld (Clangula hyemalis). The inventories are coordinated with other countries around the Baltic Sea and the North Sea through the working group JWGbird. Somateria mollissima (Anas molissima) is also monitored, but was not in the element list
Seabirds are an important part of the marine ecosystem, as most species are high up in the food chain. The monitoring of breeding and wintering birds along the coast and in the offshore areas aims to follow the population development over time, which can be affected by changing conditions in the food web but also by the direct impact that arises from a number of different human activities. The status of seabirds therefore gives a general indication of the state of the ecosystem and corresponds to the cumulative impact of different pressures. Breeding and wintering birds are nationally monitored annually along the Swedish coast. Standardized inventories of wintering birds along the coast of Sweden have been ongoing annually since 1967 and are coordinated internationally within the International Waterbird Census. Breeding birds have been monitored on a large scale since 2010. At the local level, monitoring of breeding coastal birds is also carried out in a number of coastal counties, where several of the programmes are linked to the national programme. With an approximate six-year interval, inventories of wintering seabird species in the offshore areas are carried out, in order to supplement the annual inventories. These inventories are coordinated internationally and were first carried out in 1992-93. In 2020, inventories will be carried out in the offshore sea areas within the HELCOM and OSPAR regions in order to improve knowledge of the species that live there, especially hareld (Clangula hyemalis). The inventories are coordinated with other countries around the Baltic Sea and the North Sea through the working group JWGbird. Somateria mollissima (Anas molissima) is also monitored, but was not in the element list
Seabirds are an important part of the marine ecosystem, as most species are high up in the food chain. The monitoring of breeding and wintering birds along the coast and in the offshore areas aims to follow the population development over time, which can be affected by changing conditions in the food web but also by the direct impact that arises from a number of different human activities. The status of seabirds therefore gives a general indication of the state of the ecosystem and corresponds to the cumulative impact of different pressures. Breeding and wintering birds are nationally monitored annually along the Swedish coast. Standardized inventories of wintering birds along the coast of Sweden have been ongoing annually since 1967 and are coordinated internationally within the International Waterbird Census. Breeding birds have been monitored on a large scale since 2010. At the local level, monitoring of breeding coastal birds is also carried out in a number of coastal counties, where several of the programmes are linked to the national programme. With an approximate six-year interval, inventories of wintering seabird species in the offshore areas are carried out, in order to supplement the annual inventories. These inventories are coordinated internationally and were first carried out in 1992-93. In 2020, inventories will be carried out in the offshore sea areas within the HELCOM and OSPAR regions in order to improve knowledge of the species that live there, especially hareld (Clangula hyemalis). The inventories are coordinated with other countries around the Baltic Sea and the North Sea through the working group JWGbird. Somateria mollissima (Anas molissima) is also monitored, but was not in the element list
Seabirds are an important part of the marine ecosystem, as most species are high up in the food chain. The monitoring of breeding and wintering birds along the coast and in the offshore areas aims to follow the population development over time, which can be affected by changing conditions in the food web but also by the direct impact that arises from a number of different human activities. The status of seabirds therefore gives a general indication of the state of the ecosystem and corresponds to the cumulative impact of different pressures. Breeding and wintering birds are nationally monitored annually along the Swedish coast. Standardized inventories of wintering birds along the coast of Sweden have been ongoing annually since 1967 and are coordinated internationally within the International Waterbird Census. Breeding birds have been monitored on a large scale since 2010. At the local level, monitoring of breeding coastal birds is also carried out in a number of coastal counties, where several of the programmes are linked to the national programme. With an approximate six-year interval, inventories of wintering seabird species in the offshore areas are carried out, in order to supplement the annual inventories. These inventories are coordinated internationally and were first carried out in 1992-93. In 2020, inventories will be carried out in the offshore sea areas within the HELCOM and OSPAR regions in order to improve knowledge of the species that live there, especially hareld (Clangula hyemalis). The inventories are coordinated with other countries around the Baltic Sea and the North Sea through the working group JWGbird. Somateria mollissima (Anas molissima) is also monitored, but was not in the element list
Seabirds are an important part of the marine ecosystem, as most species are high up in the food chain. The monitoring of breeding and wintering birds along the coast and in the offshore areas aims to follow the population development over time, which can be affected by changing conditions in the food web but also by the direct impact that arises from a number of different human activities. The status of seabirds therefore gives a general indication of the state of the ecosystem and corresponds to the cumulative impact of different pressures. Breeding and wintering birds are nationally monitored annually along the Swedish coast. Standardized inventories of wintering birds along the coast of Sweden have been ongoing annually since 1967 and are coordinated internationally within the International Waterbird Census. Breeding birds have been monitored on a large scale since 2010. At the local level, monitoring of breeding coastal birds is also carried out in a number of coastal counties, where several of the programmes are linked to the national programme. With an approximate six-year interval, inventories of wintering seabird species in the offshore areas are carried out, in order to supplement the annual inventories. These inventories are coordinated internationally and were first carried out in 1992-93. In 2020, inventories will be carried out in the offshore sea areas within the HELCOM and OSPAR regions in order to improve knowledge of the species that live there, especially hareld (Clangula hyemalis). The inventories are coordinated with other countries around the Baltic Sea and the North Sea through the working group JWGbird. Somateria mollissima (Anas molissima) is also monitored, but was not in the element list
Seabirds are an important part of the marine ecosystem, as most species are high up in the food chain. The monitoring of breeding and wintering birds along the coast and in the offshore areas aims to follow the population development over time, which can be affected by changing conditions in the food web but also by the direct impact that arises from a number of different human activities. The status of seabirds therefore gives a general indication of the state of the ecosystem and corresponds to the cumulative impact of different pressures. Breeding and wintering birds are nationally monitored annually along the Swedish coast. Standardized inventories of wintering birds along the coast of Sweden have been ongoing annually since 1967 and are coordinated internationally within the International Waterbird Census. Breeding birds have been monitored on a large scale since 2010. At the local level, monitoring of breeding coastal birds is also carried out in a number of coastal counties, where several of the programmes are linked to the national programme. With an approximate six-year interval, inventories of wintering seabird species in the offshore areas are carried out, in order to supplement the annual inventories. These inventories are coordinated internationally and were first carried out in 1992-93. In 2020, inventories will be carried out in the offshore sea areas within the HELCOM and OSPAR regions in order to improve knowledge of the species that live there, especially hareld (Clangula hyemalis). The inventories are coordinated with other countries around the Baltic Sea and the North Sea through the working group JWGbird. Somateria mollissima (Anas molissima) is also monitored, but was not in the element list
Seabirds are an important part of the marine ecosystem, as most species are high up in the food chain. The monitoring of breeding and wintering birds along the coast and in the offshore areas aims to follow the population development over time, which can be affected by changing conditions in the food web but also by the direct impact that arises from a number of different human activities. The status of seabirds therefore gives a general indication of the state of the ecosystem and corresponds to the cumulative impact of different pressures. Breeding and wintering birds are nationally monitored annually along the Swedish coast. Standardized inventories of wintering birds along the coast of Sweden have been ongoing annually since 1967 and are coordinated internationally within the International Waterbird Census. Breeding birds have been monitored on a large scale since 2010. At the local level, monitoring of breeding coastal birds is also carried out in a number of coastal counties, where several of the programmes are linked to the national programme. With an approximate six-year interval, inventories of wintering seabird species in the offshore areas are carried out, in order to supplement the annual inventories. These inventories are coordinated internationally and were first carried out in 1992-93. In 2020, inventories will be carried out in the offshore sea areas within the HELCOM and OSPAR regions in order to improve knowledge of the species that live there, especially hareld (Clangula hyemalis). The inventories are coordinated with other countries around the Baltic Sea and the North Sea through the working group JWGbird. Somateria mollissima (Anas molissima) is also monitored, but was not in the element list
Monitoring purpose
  • Human activities causing the pressures
  • Pressures at source
  • Human activities causing the pressures
  • Pressures at source
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Effectiveness of measures
  • Human activities causing the pressures
  • Pressures at source
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Environmental state and impacts
Other policies and conventions
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • Water Framework Directive
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • Water Framework Directive
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Birds Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Birds Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Birds Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Birds Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Birds Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Birds Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Birds Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Birds Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Birds Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Birds Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Birds Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Birds Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Birds Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Birds Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Birds Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Birds Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Birds Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Birds Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Birds Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Birds Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Birds Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
Regional cooperation - coordinating body
  • Other
  • Other
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
Regional cooperation - countries involved
Regional cooperation - implementation level
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Monitoring details
Features
Hunting and collecting for other purposes
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Fish and shellfish harvesting (professional, recreational)
Species affected by incidental by-catch
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Wading birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Wading birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Wading birds
Coastal ecosystems
Shelf ecosystems
Coastal ecosystems
Shelf ecosystems
Coastal ecosystems
Shelf ecosystems
Elements
  • Not Applicable
  • Not Applicable
  • Aythya ferina
  • Aythya fuligula
  • Aythya marila
  • Bucephala clangula
  • Clangula hyemalis
  • Melanitta fusca
  • Melanitta nigra
  • Somateria mollissima
  • Anas acuta
  • Anas clypeata
  • Anas crecca
  • Anas penelope
  • Anas platyrhynchos
  • Anas strepera
  • Anser anser
  • Branta canadensis
  • Branta leucopsis
  • Cygnus cygnus
  • Cygnus olor
  • Fulica atra
  • Alca torda
  • Cepphus grylle
  • Gavia arctica
  • Gavia stellata
  • Mergellus albellus
  • Mergus merganser
  • Mergus serrator
  • Phalacrocorax aristotelis
  • Phalacrocorax carbo
  • Podiceps auritus
  • Podiceps cristatus
  • Podiceps grisegena
  • Tachybaptus ruficollis
  • Uria aalge
  • Haliaeetus albicilla
  • Hydrocoloeus minutus
  • Hydroprogne caspia
  • Larus marinus
  • Larus ridibundus
  • Pandion haliaetus
  • Stercorarius parasiticus
  • Sterna albifrons
  • Sterna hirundo
  • Sterna paradisaea
  • Sterna sandvicensis
  • Actitis hypoleucos
  • Anthus petrosus
  • Ardea alba
  • Ardea cinerea
  • Arenaria interpres
  • Calidris alpina
  • Calidris maritima
  • Charadrius hiaticula
  • Haematopus ostralegus
  • Larus argentatus
  • Larus canus
  • Larus fuscus
  • Numenius arquata
  • Tadorna tadorna
  • Tringa totanus
  • Vanellus vanellus
  • Aythya ferina
  • Aythya fuligula
  • Aythya marila
  • Bucephala clangula
  • Clangula hyemalis
  • Melanitta fusca
  • Melanitta nigra
  • Somateria mollissima
  • Anas acuta
  • Anas clypeata
  • Anas crecca
  • Anas penelope
  • Anas platyrhynchos
  • Anas strepera
  • Anser anser
  • Branta canadensis
  • Branta leucopsis
  • Cygnus cygnus
  • Cygnus olor
  • Fulica atra
  • Alca torda
  • Cepphus grylle
  • Gavia arctica
  • Gavia stellata
  • Mergellus albellus
  • Mergus merganser
  • Mergus serrator
  • Phalacrocorax aristotelis
  • Phalacrocorax carbo
  • Podiceps auritus
  • Podiceps cristatus
  • Podiceps grisegena
  • Tachybaptus ruficollis
  • Uria aalge
  • Haliaeetus albicilla
  • Hydrocoloeus minutus
  • Hydroprogne caspia
  • Larus marinus
  • Larus ridibundus
  • Pandion haliaetus
  • Stercorarius parasiticus
  • Sterna albifrons
  • Sterna hirundo
  • Sterna paradisaea
  • Sterna sandvicensis
  • Actitis hypoleucos
  • Anthus petrosus
  • Ardea alba
  • Ardea cinerea
  • Arenaria interpres
  • Calidris alpina
  • Calidris maritima
  • Charadrius hiaticula
  • Haematopus ostralegus
  • Larus argentatus
  • Larus canus
  • Larus fuscus
  • Numenius arquata
  • Tadorna tadorna
  • Tringa totanus
  • Vanellus vanellus
  • Aythya ferina
  • Aythya fuligula
  • Aythya marila
  • Bucephala clangula
  • Clangula hyemalis
  • Melanitta fusca
  • Melanitta nigra
  • Somateria mollissima
  • Anas acuta
  • Anas clypeata
  • Anas crecca
  • Anas penelope
  • Anas platyrhynchos
  • Anas strepera
  • Anser anser
  • Branta canadensis
  • Branta leucopsis
  • Cygnus cygnus
  • Cygnus olor
  • Fulica atra
  • Alca torda
  • Cepphus grylle
  • Gavia arctica
  • Gavia stellata
  • Mergellus albellus
  • Mergus merganser
  • Mergus serrator
  • Phalacrocorax aristotelis
  • Phalacrocorax carbo
  • Podiceps auritus
  • Podiceps cristatus
  • Podiceps grisegena
  • Tachybaptus ruficollis
  • Uria aalge
  • Haliaeetus albicilla
  • Hydrocoloeus minutus
  • Hydroprogne caspia
  • Larus marinus
  • Larus ridibundus
  • Pandion haliaetus
  • Stercorarius parasiticus
  • Sterna albifrons
  • Sterna hirundo
  • Sterna paradisaea
  • Sterna sandvicensis
  • Actitis hypoleucos
  • Anthus petrosus
  • Ardea alba
  • Ardea cinerea
  • Arenaria interpres
  • Calidris alpina
  • Calidris maritima
  • Charadrius hiaticula
  • Haematopus ostralegus
  • Larus argentatus
  • Larus canus
  • Larus fuscus
  • Numenius arquata
  • Tadorna tadorna
  • Tringa totanus
  • Vanellus vanellus
  • Apex predators
  • Secondary producers
  • Apex predators
  • Secondary producers
  • Apex predators
  • Secondary producers
  • Apex predators
  • Secondary producers
  • Apex predators
  • Secondary producers
  • Apex predators
  • Secondary producers
GES criteria
NotRelevan
D1C1
D1C2
D1C2
D1C2
D1C2
D1C2
D1C3
D1C3
D1C3
D1C3
D1C3
D1C4
D1C4
D1C4
D1C4
D1C4
D4C1
D4C1
D4C2
D4C2
D4C3
D4C3
Parameters
  • Mortality (weight/volume; number of individuals)
  • Mortality (weight/volume; number of individuals)
  • Abundance (number of individuals)
  • Abundance (number of individuals)
  • Abundance (number of individuals)
  • Abundance (number of individuals)
  • Abundance (number of individuals)
  • Age distribution
  • Age distribution
  • Age distribution
  • Age distribution
  • Age distribution
  • Distribution (range)
  • Distribution (range)
  • Distribution (range)
  • Distribution (range)
  • Distribution (range)
  • Other
  • Other
  • Abundance (number of individuals)
  • Abundance (number of individuals)
  • Other
  • Other
Parameter Other
Species composition
Species composition
Species composition
Species composition
Abundance (number of individuals) Species composit
Abundance (number of individuals) Species composit
Spatial scope
  • Coastal waters (WFD)
  • Terrestrial part of MS
  • Coastal waters (WFD)
  • Terrestrial part of MS
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
Marine reporting units
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_Bottenviken
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_N_Kvarken
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_Bottenviken
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_N_Kvarken
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
Temporal scope (start date - end date)
1939-9999
1939-9999
1996-9999
1996-9999
1967-9999
1967-9999
1967-9999
1967-9999
1967-9999
1967-9999
1967-9999
1967-9999
1967-9999
1967-9999
1967-9999
1967-9999
1967-9999
1967-9999
1967-9999
1967-9999
1967-9999
1967-9999
1967-9999
1967-9999
1967-9999
Monitoring frequency
Yearly
Yearly
3-monthly
3-monthly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Monitoring type
  • Administrative data collection
  • Administrative data collection
  • Other
  • Visual observation
  • Other
  • Visual observation
  • Numerical modelling
  • Visual observation
  • Numerical modelling
  • Visual observation
  • Numerical modelling
  • Visual observation
  • Numerical modelling
  • Visual observation
  • Numerical modelling
  • Visual observation
  • Numerical modelling
  • Visual observation
  • Numerical modelling
  • Visual observation
  • Numerical modelling
  • Visual observation
  • Numerical modelling
  • Visual observation
  • Numerical modelling
  • Visual observation
  • Numerical modelling
  • Visual observation
  • Numerical modelling
  • Visual observation
  • Numerical modelling
  • Visual observation
  • Numerical modelling
  • Visual observation
  • Numerical modelling
  • Visual observation
  • Numerical modelling
  • Visual observation
  • Numerical modelling
  • Visual observation
  • Numerical modelling
  • Visual observation
  • Numerical modelling
  • Visual observation
  • Numerical modelling
  • Visual observation
  • Numerical modelling
  • Visual observation
Monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • OSPAR CEMP Guideline: Common Indicator - Marine Bird Abundance (B1) (Agreement 2016-09)
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • OSPAR CEMP Guideline: Common Indicator - Marine Bird Abundance (B1) (Agreement 2016-09)
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • OSPAR CEMP Guideline: Common Indicator - Marine Bird Abundance (B1) (Agreement 2016-09)
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • OSPAR CEMP Guideline: Common Indicator - Marine Bird Abundance (B1) (Agreement 2016-09)
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • OSPAR CEMP Guideline: Common Indicator - Marine Bird Abundance (B1) (Agreement 2016-09)
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • OSPAR CEMP Guideline: Common Indicator - Marine Bird Abundance (B1) (Agreement 2016-09)
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • OSPAR CEMP Guideline: Common Indicator - Marine Bird Abundance (B1) (Agreement 2016-09)
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • OSPAR CEMP Guideline: Common Indicator - Marine Bird Abundance (B1) (Agreement 2016-09)
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • OSPAR CEMP Guideline: Common Indicator - Marine Bird Abundance (B1) (Agreement 2016-09)
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • OSPAR CEMP Guideline: Common Indicator - Marine Bird Abundance (B1) (Agreement 2016-09)
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • OSPAR CEMP Guideline: Common Indicator - Marine Bird Abundance (B1) (Agreement 2016-09)
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • OSPAR CEMP Guideline: Common Indicator - Marine Bird Abundance (B1) (Agreement 2016-09)
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • OSPAR CEMP Guideline: Common Indicator - Marine Bird Abundance (B1) (Agreement 2016-09)
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • OSPAR CEMP Guideline: Common Indicator - Marine Bird Abundance (B1) (Agreement 2016-09)
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • OSPAR CEMP Guideline: Common Indicator - Marine Bird Abundance (B1) (Agreement 2016-09)
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • OSPAR CEMP Guideline: Common Indicator - Marine Bird Abundance (B1) (Agreement 2016-09)
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • OSPAR CEMP Guideline: Common Indicator - Marine Bird Abundance (B1) (Agreement 2016-09)
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • OSPAR CEMP Guideline: Common Indicator - Marine Bird Abundance (B1) (Agreement 2016-09)
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • OSPAR CEMP Guideline: Common Indicator - Marine Bird Abundance (B1) (Agreement 2016-09)
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • OSPAR CEMP Guideline: Common Indicator - Marine Bird Abundance (B1) (Agreement 2016-09)
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • OSPAR CEMP Guideline: Common Indicator - Marine Bird Abundance (B1) (Agreement 2016-09)
  • Other monitoring method
Monitoring method other
The collection of huntingstatistics is largely based on feedback from the hunters themselves. For example, decisions on predator control and license hunting often require reporting to the decision-making authority as soon as possible after animals have been shot in connection with the hunt. The compilation of statistics in the database ”Viltdata” is largely based on the hunters voluntarily reporting killed animals to the database.
The collection of huntingstatistics is largely based on feedback from the hunters themselves. For example, decisions on predator control and license hunting often require reporting to the decision-making authority as soon as possible after animals have been shot in connection with the hunt. The compilation of statistics in the database ”Viltdata” is largely based on the hunters voluntarily reporting killed animals to the database.
Catches and by-catches are monitored with the help of observers who accompany the fishing vessels during commercial fishing. The regular sampling is divided into area, fisheries and quarters. This means that observations are made every quarter from different types of bottom trawls (shrimp trawl, crayfish trawl with grate, trawl without grate). Usually, in the order of 0.5-2% (different for different types of fisheries) of commercial fishing trips are observed. The fishing trips observed are selected at random. Observations of by-catch within the framework of the pilot studies are carried out in the same manner. The observers examine the entire process during which the fishing gear is hauled so that also by-catches that do not follow on board but fall out of the nets can be registered. Furthermore, the observers examine the entire sorting of the catch. The observers then measure and weigh the catch and take samples for biological analysis. Remote surveillance using cameras onboard is being tested during 2020, and may supplement the monitoring in the future.
Catches and by-catches are monitored with the help of observers who accompany the fishing vessels during commercial fishing. The regular sampling is divided into area, fisheries and quarters. This means that observations are made every quarter from different types of bottom trawls (shrimp trawl, crayfish trawl with grate, trawl without grate). Usually, in the order of 0.5-2% (different for different types of fisheries) of commercial fishing trips are observed. The fishing trips observed are selected at random. Observations of by-catch within the framework of the pilot studies are carried out in the same manner. The observers examine the entire process during which the fishing gear is hauled so that also by-catches that do not follow on board but fall out of the nets can be registered. Furthermore, the observers examine the entire sorting of the catch. The observers then measure and weigh the catch and take samples for biological analysis. Remote surveillance using cameras onboard is being tested during 2020, and may supplement the monitoring in the future.
"Wintering birds: https://www.diva-portal.org/smash/get/diva2:1172153/FULLTEXT01.pdf Breeding birds: https://www.fageltaxering.lu.se/inventera/metoder/kustfagelrutorna/metodik-kustfagelrutor"
"Wintering birds: https://www.diva-portal.org/smash/get/diva2:1172153/FULLTEXT01.pdf Breeding birds: https://www.fageltaxering.lu.se/inventera/metoder/kustfagelrutorna/metodik-kustfagelrutor"
"Wintering birds: https://www.diva-portal.org/smash/get/diva2:1172153/FULLTEXT01.pdf Breeding birds: https://www.fageltaxering.lu.se/inventera/metoder/kustfagelrutorna/metodik-kustfagelrutor"
"Wintering birds: https://www.diva-portal.org/smash/get/diva2:1172153/FULLTEXT01.pdf Breeding birds: https://www.fageltaxering.lu.se/inventera/metoder/kustfagelrutorna/metodik-kustfagelrutor"
"Wintering birds: https://www.diva-portal.org/smash/get/diva2:1172153/FULLTEXT01.pdf Breeding birds: https://www.fageltaxering.lu.se/inventera/metoder/kustfagelrutorna/metodik-kustfagelrutor"
"Wintering birds: https://www.diva-portal.org/smash/get/diva2:1172153/FULLTEXT01.pdf Breeding birds: https://www.fageltaxering.lu.se/inventera/metoder/kustfagelrutorna/metodik-kustfagelrutor"
"Wintering birds: https://www.diva-portal.org/smash/get/diva2:1172153/FULLTEXT01.pdf Breeding birds: https://www.fageltaxering.lu.se/inventera/metoder/kustfagelrutorna/metodik-kustfagelrutor"
"Wintering birds: https://www.diva-portal.org/smash/get/diva2:1172153/FULLTEXT01.pdf Breeding birds: https://www.fageltaxering.lu.se/inventera/metoder/kustfagelrutorna/metodik-kustfagelrutor"
"Wintering birds: https://www.diva-portal.org/smash/get/diva2:1172153/FULLTEXT01.pdf Breeding birds: https://www.fageltaxering.lu.se/inventera/metoder/kustfagelrutorna/metodik-kustfagelrutor"
"Wintering birds: https://www.diva-portal.org/smash/get/diva2:1172153/FULLTEXT01.pdf Breeding birds: https://www.fageltaxering.lu.se/inventera/metoder/kustfagelrutorna/metodik-kustfagelrutor"
"Wintering birds: https://www.diva-portal.org/smash/get/diva2:1172153/FULLTEXT01.pdf Breeding birds: https://www.fageltaxering.lu.se/inventera/metoder/kustfagelrutorna/metodik-kustfagelrutor"
"Wintering birds: https://www.diva-portal.org/smash/get/diva2:1172153/FULLTEXT01.pdf Breeding birds: https://www.fageltaxering.lu.se/inventera/metoder/kustfagelrutorna/metodik-kustfagelrutor"
"Wintering birds: https://www.diva-portal.org/smash/get/diva2:1172153/FULLTEXT01.pdf Breeding birds: https://www.fageltaxering.lu.se/inventera/metoder/kustfagelrutorna/metodik-kustfagelrutor"
"Wintering birds: https://www.diva-portal.org/smash/get/diva2:1172153/FULLTEXT01.pdf Breeding birds: https://www.fageltaxering.lu.se/inventera/metoder/kustfagelrutorna/metodik-kustfagelrutor"
"Wintering birds: https://www.diva-portal.org/smash/get/diva2:1172153/FULLTEXT01.pdf Breeding birds: https://www.fageltaxering.lu.se/inventera/metoder/kustfagelrutorna/metodik-kustfagelrutor"
"Wintering birds: https://www.diva-portal.org/smash/get/diva2:1172153/FULLTEXT01.pdf Breeding birds: https://www.fageltaxering.lu.se/inventera/metoder/kustfagelrutorna/metodik-kustfagelrutor"
"Wintering birds: https://www.diva-portal.org/smash/get/diva2:1172153/FULLTEXT01.pdf Breeding birds: https://www.fageltaxering.lu.se/inventera/metoder/kustfagelrutorna/metodik-kustfagelrutor"
"Wintering birds: https://www.diva-portal.org/smash/get/diva2:1172153/FULLTEXT01.pdf Breeding birds: https://www.fageltaxering.lu.se/inventera/metoder/kustfagelrutorna/metodik-kustfagelrutor"
"Wintering birds: https://www.diva-portal.org/smash/get/diva2:1172153/FULLTEXT01.pdf Breeding birds: https://www.fageltaxering.lu.se/inventera/metoder/kustfagelrutorna/metodik-kustfagelrutor"
"Wintering birds: https://www.diva-portal.org/smash/get/diva2:1172153/FULLTEXT01.pdf Breeding birds: https://www.fageltaxering.lu.se/inventera/metoder/kustfagelrutorna/metodik-kustfagelrutor"
"Wintering birds: https://www.diva-portal.org/smash/get/diva2:1172153/FULLTEXT01.pdf Breeding birds: https://www.fageltaxering.lu.se/inventera/metoder/kustfagelrutorna/metodik-kustfagelrutor"
Quality control
In order to assess the reliability of the hunting statistics, the responsible authority can check that the statistics do not deviate in any improbable way. Furthermore, the various reporting requirements and the design of the decisions constitute a quality assurance in itself.
In order to assess the reliability of the hunting statistics, the responsible authority can check that the statistics do not deviate in any improbable way. Furthermore, the various reporting requirements and the design of the decisions constitute a quality assurance in itself.
Sampling takes place through a random selection of ships/voyages. The observers bring with them a manual for determining the species of birds and also photograph captured birds as much as possible. Data is registered in the national database Fiskdata2 according to the updated manual. Data is examined and checked in several respects. Quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers).
Sampling takes place through a random selection of ships/voyages. The observers bring with them a manual for determining the species of birds and also photograph captured birds as much as possible. Data is registered in the national database Fiskdata2 according to the updated manual. Data is examined and checked in several respects. Quality assurance includes control reading routines of entered data against protocols, automatic quality control of data within the database and manual quality control of data (identification of outliers).
The inventories of wintering and breeding seabirds follow a simple and well-documented methodology. Reporting is done via digital protocols that are sent to the Swedish Bird Taxation, which is the project manager for both inventories. Received protocols are checked before they are entered into the database. In case of doubt, they contact the rapporter. Furthermore, entered data is validated through a number of control questions.
The inventories of wintering and breeding seabirds follow a simple and well-documented methodology. Reporting is done via digital protocols that are sent to the Swedish Bird Taxation, which is the project manager for both inventories. Received protocols are checked before they are entered into the database. In case of doubt, they contact the rapporter. Furthermore, entered data is validated through a number of control questions.
The inventories of wintering and breeding seabirds follow a simple and well-documented methodology. Reporting is done via digital protocols that are sent to the Swedish Bird Taxation, which is the project manager for both inventories. Received protocols are checked before they are entered into the database. In case of doubt, they contact the rapporter. Furthermore, entered data is validated through a number of control questions.
The inventories of wintering and breeding seabirds follow a simple and well-documented methodology. Reporting is done via digital protocols that are sent to the Swedish Bird Taxation, which is the project manager for both inventories. Received protocols are checked before they are entered into the database. In case of doubt, they contact the rapporter. Furthermore, entered data is validated through a number of control questions.
The inventories of wintering and breeding seabirds follow a simple and well-documented methodology. Reporting is done via digital protocols that are sent to the Swedish Bird Taxation, which is the project manager for both inventories. Received protocols are checked before they are entered into the database. In case of doubt, they contact the rapporter. Furthermore, entered data is validated through a number of control questions.
The inventories of wintering and breeding seabirds follow a simple and well-documented methodology. Reporting is done via digital protocols that are sent to the Swedish Bird Taxation, which is the project manager for both inventories. Received protocols are checked before they are entered into the database. In case of doubt, they contact the rapporter. Furthermore, entered data is validated through a number of control questions.
The inventories of wintering and breeding seabirds follow a simple and well-documented methodology. Reporting is done via digital protocols that are sent to the Swedish Bird Taxation, which is the project manager for both inventories. Received protocols are checked before they are entered into the database. In case of doubt, they contact the rapporter. Furthermore, entered data is validated through a number of control questions.
The inventories of wintering and breeding seabirds follow a simple and well-documented methodology. Reporting is done via digital protocols that are sent to the Swedish Bird Taxation, which is the project manager for both inventories. Received protocols are checked before they are entered into the database. In case of doubt, they contact the rapporter. Furthermore, entered data is validated through a number of control questions.
The inventories of wintering and breeding seabirds follow a simple and well-documented methodology. Reporting is done via digital protocols that are sent to the Swedish Bird Taxation, which is the project manager for both inventories. Received protocols are checked before they are entered into the database. In case of doubt, they contact the rapporter. Furthermore, entered data is validated through a number of control questions.
The inventories of wintering and breeding seabirds follow a simple and well-documented methodology. Reporting is done via digital protocols that are sent to the Swedish Bird Taxation, which is the project manager for both inventories. Received protocols are checked before they are entered into the database. In case of doubt, they contact the rapporter. Furthermore, entered data is validated through a number of control questions.
The inventories of wintering and breeding seabirds follow a simple and well-documented methodology. Reporting is done via digital protocols that are sent to the Swedish Bird Taxation, which is the project manager for both inventories. Received protocols are checked before they are entered into the database. In case of doubt, they contact the rapporter. Furthermore, entered data is validated through a number of control questions.
The inventories of wintering and breeding seabirds follow a simple and well-documented methodology. Reporting is done via digital protocols that are sent to the Swedish Bird Taxation, which is the project manager for both inventories. Received protocols are checked before they are entered into the database. In case of doubt, they contact the rapporter. Furthermore, entered data is validated through a number of control questions.
The inventories of wintering and breeding seabirds follow a simple and well-documented methodology. Reporting is done via digital protocols that are sent to the Swedish Bird Taxation, which is the project manager for both inventories. Received protocols are checked before they are entered into the database. In case of doubt, they contact the rapporter. Furthermore, entered data is validated through a number of control questions.
The inventories of wintering and breeding seabirds follow a simple and well-documented methodology. Reporting is done via digital protocols that are sent to the Swedish Bird Taxation, which is the project manager for both inventories. Received protocols are checked before they are entered into the database. In case of doubt, they contact the rapporter. Furthermore, entered data is validated through a number of control questions.
The inventories of wintering and breeding seabirds follow a simple and well-documented methodology. Reporting is done via digital protocols that are sent to the Swedish Bird Taxation, which is the project manager for both inventories. Received protocols are checked before they are entered into the database. In case of doubt, they contact the rapporter. Furthermore, entered data is validated through a number of control questions.
The inventories of wintering and breeding seabirds follow a simple and well-documented methodology. Reporting is done via digital protocols that are sent to the Swedish Bird Taxation, which is the project manager for both inventories. Received protocols are checked before they are entered into the database. In case of doubt, they contact the rapporter. Furthermore, entered data is validated through a number of control questions.
The inventories of wintering and breeding seabirds follow a simple and well-documented methodology. Reporting is done via digital protocols that are sent to the Swedish Bird Taxation, which is the project manager for both inventories. Received protocols are checked before they are entered into the database. In case of doubt, they contact the rapporter. Furthermore, entered data is validated through a number of control questions.
The inventories of wintering and breeding seabirds follow a simple and well-documented methodology. Reporting is done via digital protocols that are sent to the Swedish Bird Taxation, which is the project manager for both inventories. Received protocols are checked before they are entered into the database. In case of doubt, they contact the rapporter. Furthermore, entered data is validated through a number of control questions.
The inventories of wintering and breeding seabirds follow a simple and well-documented methodology. Reporting is done via digital protocols that are sent to the Swedish Bird Taxation, which is the project manager for both inventories. Received protocols are checked before they are entered into the database. In case of doubt, they contact the rapporter. Furthermore, entered data is validated through a number of control questions.
The inventories of wintering and breeding seabirds follow a simple and well-documented methodology. Reporting is done via digital protocols that are sent to the Swedish Bird Taxation, which is the project manager for both inventories. Received protocols are checked before they are entered into the database. In case of doubt, they contact the rapporter. Furthermore, entered data is validated through a number of control questions.
The inventories of wintering and breeding seabirds follow a simple and well-documented methodology. Reporting is done via digital protocols that are sent to the Swedish Bird Taxation, which is the project manager for both inventories. Received protocols are checked before they are entered into the database. In case of doubt, they contact the rapporter. Furthermore, entered data is validated through a number of control questions.
Data management
Statistics on killed animals in predator control and license hunting are available from the respective responsible authority and can be made available on request. Statistics on license and general hunting can be found in the Swedish Hunters' Association's database ”Viltdata”.
Statistics on killed animals in predator control and license hunting are available from the respective responsible authority and can be made available on request. Statistics on license and general hunting can be found in the Swedish Hunters' Association's database ”Viltdata”.
A data hosting agreement with Lund University has been developed and work begun in 2019 to make large parts of the data publicly available and downloadable. Data from the winter counts are also available from the international coordinator of seabird inventories - Wetlands International. Data are fully available and can be obtained via contact with Swedish bird taxation via fageltaxering@biol.lu.se.
A data hosting agreement with Lund University has been developed and work begun in 2019 to make large parts of the data publicly available and downloadable. Data from the winter counts are also available from the international coordinator of seabird inventories - Wetlands International. Data are fully available and can be obtained via contact with Swedish bird taxation via fageltaxering@biol.lu.se.
A data hosting agreement with Lund University has been developed and work begun in 2019 to make large parts of the data publicly available and downloadable. Data from the winter counts are also available from the international coordinator of seabird inventories - Wetlands International. Data are fully available and can be obtained via contact with Swedish bird taxation via fageltaxering@biol.lu.se.
A data hosting agreement with Lund University has been developed and work begun in 2019 to make large parts of the data publicly available and downloadable. Data from the winter counts are also available from the international coordinator of seabird inventories - Wetlands International. Data are fully available and can be obtained via contact with Swedish bird taxation via fageltaxering@biol.lu.se.
A data hosting agreement with Lund University has been developed and work begun in 2019 to make large parts of the data publicly available and downloadable. Data from the winter counts are also available from the international coordinator of seabird inventories - Wetlands International. Data are fully available and can be obtained via contact with Swedish bird taxation via fageltaxering@biol.lu.se.
A data hosting agreement with Lund University has been developed and work begun in 2019 to make large parts of the data publicly available and downloadable. Data from the winter counts are also available from the international coordinator of seabird inventories - Wetlands International. Data are fully available and can be obtained via contact with Swedish bird taxation via fageltaxering@biol.lu.se.
A data hosting agreement with Lund University has been developed and work begun in 2019 to make large parts of the data publicly available and downloadable. Data from the winter counts are also available from the international coordinator of seabird inventories - Wetlands International. Data are fully available and can be obtained via contact with Swedish bird taxation via fageltaxering@biol.lu.se.
A data hosting agreement with Lund University has been developed and work begun in 2019 to make large parts of the data publicly available and downloadable. Data from the winter counts are also available from the international coordinator of seabird inventories - Wetlands International. Data are fully available and can be obtained via contact with Swedish bird taxation via fageltaxering@biol.lu.se.
A data hosting agreement with Lund University has been developed and work begun in 2019 to make large parts of the data publicly available and downloadable. Data from the winter counts are also available from the international coordinator of seabird inventories - Wetlands International. Data are fully available and can be obtained via contact with Swedish bird taxation via fageltaxering@biol.lu.se.
A data hosting agreement with Lund University has been developed and work begun in 2019 to make large parts of the data publicly available and downloadable. Data from the winter counts are also available from the international coordinator of seabird inventories - Wetlands International. Data are fully available and can be obtained via contact with Swedish bird taxation via fageltaxering@biol.lu.se.
A data hosting agreement with Lund University has been developed and work begun in 2019 to make large parts of the data publicly available and downloadable. Data from the winter counts are also available from the international coordinator of seabird inventories - Wetlands International. Data are fully available and can be obtained via contact with Swedish bird taxation via fageltaxering@biol.lu.se.
A data hosting agreement with Lund University has been developed and work begun in 2019 to make large parts of the data publicly available and downloadable. Data from the winter counts are also available from the international coordinator of seabird inventories - Wetlands International. Data are fully available and can be obtained via contact with Swedish bird taxation via fageltaxering@biol.lu.se.
A data hosting agreement with Lund University has been developed and work begun in 2019 to make large parts of the data publicly available and downloadable. Data from the winter counts are also available from the international coordinator of seabird inventories - Wetlands International. Data are fully available and can be obtained via contact with Swedish bird taxation via fageltaxering@biol.lu.se.
A data hosting agreement with Lund University has been developed and work begun in 2019 to make large parts of the data publicly available and downloadable. Data from the winter counts are also available from the international coordinator of seabird inventories - Wetlands International. Data are fully available and can be obtained via contact with Swedish bird taxation via fageltaxering@biol.lu.se.
A data hosting agreement with Lund University has been developed and work begun in 2019 to make large parts of the data publicly available and downloadable. Data from the winter counts are also available from the international coordinator of seabird inventories - Wetlands International. Data are fully available and can be obtained via contact with Swedish bird taxation via fageltaxering@biol.lu.se.
A data hosting agreement with Lund University has been developed and work begun in 2019 to make large parts of the data publicly available and downloadable. Data from the winter counts are also available from the international coordinator of seabird inventories - Wetlands International. Data are fully available and can be obtained via contact with Swedish bird taxation via fageltaxering@biol.lu.se.
A data hosting agreement with Lund University has been developed and work begun in 2019 to make large parts of the data publicly available and downloadable. Data from the winter counts are also available from the international coordinator of seabird inventories - Wetlands International. Data are fully available and can be obtained via contact with Swedish bird taxation via fageltaxering@biol.lu.se.
A data hosting agreement with Lund University has been developed and work begun in 2019 to make large parts of the data publicly available and downloadable. Data from the winter counts are also available from the international coordinator of seabird inventories - Wetlands International. Data are fully available and can be obtained via contact with Swedish bird taxation via fageltaxering@biol.lu.se.
A data hosting agreement with Lund University has been developed and work begun in 2019 to make large parts of the data publicly available and downloadable. Data from the winter counts are also available from the international coordinator of seabird inventories - Wetlands International. Data are fully available and can be obtained via contact with Swedish bird taxation via fageltaxering@biol.lu.se.
A data hosting agreement with Lund University has been developed and work begun in 2019 to make large parts of the data publicly available and downloadable. Data from the winter counts are also available from the international coordinator of seabird inventories - Wetlands International. Data are fully available and can be obtained via contact with Swedish bird taxation via fageltaxering@biol.lu.se.
A data hosting agreement with Lund University has been developed and work begun in 2019 to make large parts of the data publicly available and downloadable. Data from the winter counts are also available from the international coordinator of seabird inventories - Wetlands International. Data are fully available and can be obtained via contact with Swedish bird taxation via fageltaxering@biol.lu.se.
Data access
Related indicator/name
  • BALSE-1.1A_Bif�ngst_tumlare
  • BALSE-1.1A_Bif�ngst_tumlare
  • ANSSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2B_Abund_�vervintrande_f�gel
  • BALSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2B_Abund_�vervintrande_f�gel
  • BALSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2B_Abund_�vervintrande_f�gel
  • BALSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2B_Abund_�vervintrande_f�gel
  • BALSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2B_Abund_�vervintrande_f�gel
  • BALSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2B_Abund_�vervintrande_f�gel
  • BALSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2B_Abund_�vervintrande_f�gel
  • BALSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2B_Abund_�vervintrande_f�gel
  • BALSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2B_Abund_�vervintrande_f�gel
  • BALSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2B_Abund_�vervintrande_f�gel
  • BALSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2B_Abund_�vervintrande_f�gel
  • BALSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2B_Abund_�vervintrande_f�gel
  • BALSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2B_Abund_�vervintrande_f�gel
  • BALSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2B_Abund_�vervintrande_f�gel
  • BALSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2B_Abund_�vervintrande_f�gel
  • BALSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2B_Abund_�vervintrande_f�gel
  • BALSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2B_Abund_�vervintrande_f�gel
  • BALSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2B_Abund_�vervintrande_f�gel
  • BALSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2B_Abund_�vervintrande_f�gel
  • BALSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2B_Abund_�vervintrande_f�gel
  • BALSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2A_Abund_h�ckande_f�gel
  • ANSSE-1.2B_Abund_�vervintrande_f�gel
  • BALSE-1.2A_Abund_h�ckande_f�gel
Contact
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
References