Member State report / Art11 / 2014-2020 / D1-B / Finland / Baltic Sea

Report type Member State report to Commission
MSFD Article Art. 11 Monitoring programmes (and Art. 17 updates)
Report due 2014-10-15; 2020-10-15
GES Descriptor D1 Birds
Member State Finland
Region/subregion Baltic Sea
Reported by Reporter not found
Report date Date not found; 2020-10-31
Report access
2014 data
2020 data
Monitoring programme Monitoring programme name
MP_D1_4_6_Birds
MP_D1_4_6_Birds
MP_D1_4_6_Birds
MP_D1_4_6_Birds
MP_D1_4_6_Birds
MP_D1_4_6_Fish
MP_D1_4_6_Fish
MP_D1_4_6_Fish
MP_D1_4_6_Mammals
MP_D1_4_6_Mammals
MP_D1_4_6_SeabedHabitats
MP_D1_4_6_SeabedHabitats
MP_D1_4_6_SeabedHabitats
MP_D1_4_6_SeabedHabitats
MP_D3
MP_D3
Monitoring programme Reference existing programme
BALFI-D01,04,06fis
BALFI-D01,04,06fis
BALFI-D01,04,06fis
BALFI-D01,04,06ben
BALFI-D01,04,06ben
BALFI-D01,04,06ben
BALFI-D01,04,06ben
Monitoring programme Marine Unit ID
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
Q4e - Programme ID
BALFI-D01,04,06bir
BALFI-D01,04,06bir
BALFI-D01,04,06bir
BALFI-D01,04,06bir
BALFI-D01,04,06bir
BALFI-D01,04,06fis
BALFI-D01,04,06fis
BALFI-D01,04,06fis
BALFI-D01,04,06mam
BALFI-D01,04,06mam
BALFI-D01,04,06ben
BALFI-D01,04,06ben
BALFI-D01,04,06ben
BALFI-D01,04,06ben
BALFI-D03
BALFI-D03
Q4f - Programme description
General information is available in the HELCOM Monitoring manual (Biodiversity-Birds) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#Birds General information on Sub-programmes is available in the HELCOM Monitoring manual at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/
General information is available in the HELCOM Monitoring manual (Biodiversity-Birds) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#Birds General information on Sub-programmes is available in the HELCOM Monitoring manual at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/
General information is available in the HELCOM Monitoring manual (Biodiversity-Birds) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#Birds General information on Sub-programmes is available in the HELCOM Monitoring manual at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/
General information is available in the HELCOM Monitoring manual (Biodiversity-Birds) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#Birds General information on Sub-programmes is available in the HELCOM Monitoring manual at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/
General information is available in the HELCOM Monitoring manual (Biodiversity-Birds) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#Birds General information on Sub-programmes is available in the HELCOM Monitoring manual at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/
General information is available in the HELCOM Monitoring manual (Biodiversity, Fish) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#Fish General information on Sub-programmes (Fish and Fisheries) is available in the HELCOM Monitoring manual at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/
General information is available in the HELCOM Monitoring manual (Biodiversity, Fish) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#Fish General information on Sub-programmes (Fish and Fisheries) is available in the HELCOM Monitoring manual at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/
General information is available in the HELCOM Monitoring manual (Biodiversity, Fish) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#Fish General information on Sub-programmes (Fish and Fisheries) is available in the HELCOM Monitoring manual at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/
General information is available in the HELCOM Monitoring manual - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#Mammals General information on Sub-programs is available in the HELCOM Monitoring manual - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/
General information is available in the HELCOM Monitoring manual - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#Mammals General information on Sub-programs is available in the HELCOM Monitoring manual - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/
General information is available in the HELCOM Monitoring manual (Biodiversity - Seabed habitats) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#SeabedHabitats General information on Sub-programmes (Seabed habitat distribution and extent) is available in the HELCOM Monitoring manual at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/
General information is available in the HELCOM Monitoring manual (Biodiversity - Seabed habitats) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#SeabedHabitats General information on Sub-programmes (Seabed habitat distribution and extent) is available in the HELCOM Monitoring manual at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/
General information is available in the HELCOM Monitoring manual (Biodiversity - Seabed habitats) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#SeabedHabitats General information on Sub-programmes (Seabed habitat distribution and extent) is available in the HELCOM Monitoring manual at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/
General information is available in the HELCOM Monitoring manual (Biodiversity - Seabed habitats) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#SeabedHabitats General information on Sub-programmes (Seabed habitat distribution and extent) is available in the HELCOM Monitoring manual at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/
General information on monitoring of fish and fisheries is available at: HELCOM Monitoring manual - Monitoring of “Fish, fisheries and shellfish” - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/ HELCOM Monitoring manual Sub-program: Coastal fish, where information can be found in the section "Monitoring requirements" - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish HELCOM Monitoring manual Sub-program: Migratory fish, where information can be found in the section "Monitoring requirements" - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/migratory-fish HELCOM Monitoring manual Sub-program: Offshore fish, where information can be found in the section "Monitoring requirements" - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish
General information on monitoring of fish and fisheries is available at: HELCOM Monitoring manual - Monitoring of “Fish, fisheries and shellfish” - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/ HELCOM Monitoring manual Sub-program: Coastal fish, where information can be found in the section "Monitoring requirements" - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish HELCOM Monitoring manual Sub-program: Migratory fish, where information can be found in the section "Monitoring requirements" - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/migratory-fish HELCOM Monitoring manual Sub-program: Offshore fish, where information can be found in the section "Monitoring requirements" - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish
Q5e - Natural variability
  • Quantiative
  • Quantiative
  • Quantiative
  • Quantiative
  • Quantiative
  • Qualitative
  • Quantiative
  • Qualitative
  • Quantiative
  • Qualitative
  • Quantiative
  • Quantiative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
  • ExpertOpinion
  • Qualitative
  • Quantiative
Q5d - Adequacy for assessment of GES Q5d - Adequate data
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Q5d - Adequacy for assessment of GES Q5d - Established methods
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Q5d - Adequacy for assessment of GES Q5d - Adequate understanding of GES
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Q5d - Adequacy for assessment of GES Q5d - Adequate capacity
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Q5f - Description of programme for GES assessment
The monitoring supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability.
The monitoring supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability.
The monitoring supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability.
The monitoring supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability.
The monitoring supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability.
The monitoring supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability.
The monitoring supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability.
The monitoring supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability.
The monitoring supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability.
The monitoring supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability.
The monitoring supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability. The monitoring of benthic fauna and flora is established; currently biotopes are being monitored through this monitoring. The Finnish underwater nature mapping program (VELMU) has mapped all benthic biotopes which serves as a baseline for monitoring of the remaining biotopes, which will be assessed by 2018 on the basis of this mapping.
The monitoring supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability. The monitoring of benthic fauna and flora is established; currently biotopes are being monitored through this monitoring. The Finnish underwater nature mapping program (VELMU) has mapped all benthic biotopes which serves as a baseline for monitoring of the remaining biotopes, which will be assessed by 2018 on the basis of this mapping.
The monitoring supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability. The monitoring of benthic fauna and flora is established; currently biotopes are being monitored through this monitoring. The Finnish underwater nature mapping program (VELMU) has mapped all benthic biotopes which serves as a baseline for monitoring of the remaining biotopes, which will be assessed by 2018 on the basis of this mapping.
The monitoring supports indicators which measure the distance to GES. The monitoring is sufficient to detect the natural variability. The monitoring of benthic fauna and flora is established; currently biotopes are being monitored through this monitoring. The Finnish underwater nature mapping program (VELMU) has mapped all benthic biotopes which serves as a baseline for monitoring of the remaining biotopes, which will be assessed by 2018 on the basis of this mapping.
As reported for Art. 9 and 10, the threshold values for GES are: The level of pressure of the fishing activity is not exceeding MSY-level, and the reproductive capacity of the fish populations is secured. Both sub-programmes under this programme are sufficient to produce data on target species populations which are under international regulation. The data, which is collected within the sub-programmes, gives reliable information on population dynamics caused by fishing and natural factors. The program provides information for the descriptor 3 (MSD-criteria 3.1, 3.2 and 3.3), and as for salmon, for the descriptor 1 (MSD criteria 1.2 and 1.3). The program also collects information on fishing pressure.
As reported for Art. 9 and 10, the threshold values for GES are: The level of pressure of the fishing activity is not exceeding MSY-level, and the reproductive capacity of the fish populations is secured. Both sub-programmes under this programme are sufficient to produce data on target species populations which are under international regulation. The data, which is collected within the sub-programmes, gives reliable information on population dynamics caused by fishing and natural factors. The program provides information for the descriptor 3 (MSD-criteria 3.1, 3.2 and 3.3), and as for salmon, for the descriptor 1 (MSD criteria 1.2 and 1.3). The program also collects information on fishing pressure.
Q5g - Gap-filling date for GES assessment
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
Q5h - Plans to implement monitoring for GES assessment
No immediate development needs.
No immediate development needs.
No immediate development needs.
No immediate development needs.
No immediate development needs.
No immediate development needs.
No immediate development needs.
No immediate development needs.
No immediate development needs.
No immediate development needs.
Benthic biotope monitoring will be further developed for the next monitoring cycle based on the baseline mapping.
Benthic biotope monitoring will be further developed for the next monitoring cycle based on the baseline mapping.
Benthic biotope monitoring will be further developed for the next monitoring cycle based on the baseline mapping.
Benthic biotope monitoring will be further developed for the next monitoring cycle based on the baseline mapping.
No immediate development needs.
No immediate development needs.
Q6a -Relevant targets Q6a - Environmental target
Target 01 Target 02 Target 04 Target 17 Target 30
Target 01 Target 02 Target 04 Target 17 Target 30
Target 01 Target 02 Target 04 Target 17 Target 30
Target 01 Target 02 Target 04 Target 17 Target 30
Target 01 Target 02 Target 04 Target 17 Target 30
Target 01 Target 02 Target 05 Target 13 Target 15 Target 16 Target 18
Target 01 Target 02 Target 05 Target 13 Target 15 Target 16 Target 18
Target 01 Target 02 Target 05 Target 13 Target 15 Target 16 Target 18
Target 01 Target 02 Target 03 Target 17 Target 30
Target 01 Target 02 Target 03 Target 17 Target 30
Target 06 Target 07 Target 08 Target 09 Target 10 Target 20 Target 24 Target 25 Target 26
Target 06 Target 07 Target 08 Target 09 Target 10 Target 20 Target 24 Target 25 Target 26
Target 06 Target 07 Target 08 Target 09 Target 10 Target 20 Target 24 Target 25 Target 26
Target 06 Target 07 Target 08 Target 09 Target 10 Target 20 Target 24 Target 25 Target 26
Target 12 Target 13 Target 14 Target 15 Target 16
Target 12 Target 13 Target 14 Target 15 Target 16
Q6a -Relevant targets Q6a - Associated indicator
Target 01 Target 02 Target 04 Target 17 Target 30
Target 01 Target 02 Target 04 Target 17 Target 30
Target 01 Target 02 Target 04 Target 17 Target 30
Target 01 Target 02 Target 04 Target 17 Target 30
Target 01 Target 02 Target 04 Target 17 Target 30
Target 01 Target 02 Target 05 Target 13 Target 15 Target 16 Target 18
Target 01 Target 02 Target 05 Target 13 Target 15 Target 16 Target 18
Target 01 Target 02 Target 05 Target 13 Target 15 Target 16 Target 18
Target 01 Target 02 Target 03 Target 17 Target 30
Target 01 Target 02 Target 03 Target 17 Target 30
Target 06 Target 08 Target 09 Target 10 Target 20 Target 24 Target 25 Target 26
Target 06 Target 08 Target 09 Target 10 Target 20 Target 24 Target 25 Target 26
Target 06 Target 08 Target 09 Target 10 Target 20 Target 24 Target 25 Target 26
Target 06 Target 08 Target 09 Target 10 Target 20 Target 24 Target 25 Target 26
Target 12 Target 13 Target 14 Target 15 Target 16
Target 12 Target 13 Target 14 Target 15 Target 16
Q6b - Adequacy for assessment of targets Q6b_SuitableData
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Q6b - Adequacy for assessment of targets Q6b_EstablishedMethods
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Q6b - Adequacy for assessment of targets Q6d_AdequateCapacity
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Q6c - Target updating
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Y
Q6d - Description of programme for targets assessment
The progress towards the target will be monitored by a number of indicators (see Finnish Art. 10 report)
The progress towards the target will be monitored by a number of indicators (see Finnish Art. 10 report)
The progress towards the target will be monitored by a number of indicators (see Finnish Art. 10 report)
The progress towards the target will be monitored by a number of indicators (see Finnish Art. 10 report)
The progress towards the target will be monitored by a number of indicators (see Finnish Art. 10 report)
The progress towards the target will be monitored by a number of indicators (see Finnish Art. 10 report)
The progress towards the target will be monitored by a number of indicators (see Finnish Art. 10 report)
The progress towards the target will be monitored by a number of indicators (see Finnish Art. 10 report)
The progress towards the target will be monitored by a number of indicators (see Finnish Art. 10 report)
The progress towards the target will be monitored by a number of indicators (see Finnish Art. 10 report)
The progress towards the target will be monitored by a number of indicators (see Finnish Art. 10 report)
The progress towards the target will be monitored by a number of indicators (see Finnish Art. 10 report)
The progress towards the target will be monitored by a number of indicators (see Finnish Art. 10 report)
The progress towards the target will be monitored by a number of indicators (see Finnish Art. 10 report)
The progress towards the targets will be monitored by a number of indicators.
The progress towards the targets will be monitored by a number of indicators.
Q6e - Gap-filling date for targets assessment
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
Q6f - Plans to implement monitoring for targets assessment
Program is fully adequate
Program is fully adequate
Q7a - Relevant activities
  • Hunting
  • UsesActivitiesOther
  • Hunting
  • UsesActivitiesOther
  • Hunting
  • UsesActivitiesOther
  • Hunting
  • UsesActivitiesOther
  • Hunting
  • UsesActivitiesOther
  • CablesPipelines
  • Dredging
  • MiningSandGravel
  • OffshoreStructures
  • Ports
  • RenewableEnergy
  • Shipping
  • SolidWasteDisposal
  • CablesPipelines
  • Dredging
  • MiningSandGravel
  • OffshoreStructures
  • Ports
  • RenewableEnergy
  • Shipping
  • SolidWasteDisposal
  • CablesPipelines
  • Dredging
  • MiningSandGravel
  • OffshoreStructures
  • Ports
  • RenewableEnergy
  • Shipping
  • SolidWasteDisposal
  • CablesPipelines
  • Dredging
  • MiningSandGravel
  • OffshoreStructures
  • Ports
  • RenewableEnergy
  • Shipping
  • SolidWasteDisposal
  • Fisheries
  • Fisheries
Q7b - Description of monitoring of activities
Hunting of sea-birds and Grey Seal is practiced in the whole coastal area. The hunting focuses on certain game species. Hunting of Grey Seal requires permit and a quota is set annually. The monitoring collects all game statistics.
Hunting of sea-birds and Grey Seal is practiced in the whole coastal area. The hunting focuses on certain game species. Hunting of Grey Seal requires permit and a quota is set annually. The monitoring collects all game statistics.
Hunting of sea-birds and Grey Seal is practiced in the whole coastal area. The hunting focuses on certain game species. Hunting of Grey Seal requires permit and a quota is set annually. The monitoring collects all game statistics.
Hunting of sea-birds and Grey Seal is practiced in the whole coastal area. The hunting focuses on certain game species. Hunting of Grey Seal requires permit and a quota is set annually. The monitoring collects all game statistics.
Hunting of sea-birds and Grey Seal is practiced in the whole coastal area. The hunting focuses on certain game species. Hunting of Grey Seal requires permit and a quota is set annually. The monitoring collects all game statistics.
No monitoring of activities
No monitoring of activities
No monitoring of activities
No monitoring activities
No monitoring activities
Data collected from licensing authorities (eg. constructions, dredging) and automatic identification system (AIS) is used in an assessment of pressures by HELCOM in the Baltic Sea region. HELCOM cumulative impact assessments have identified the impacts of activities on marine environment.
Data collected from licensing authorities (eg. constructions, dredging) and automatic identification system (AIS) is used in an assessment of pressures by HELCOM in the Baltic Sea region. HELCOM cumulative impact assessments have identified the impacts of activities on marine environment.
Data collected from licensing authorities (eg. constructions, dredging) and automatic identification system (AIS) is used in an assessment of pressures by HELCOM in the Baltic Sea region. HELCOM cumulative impact assessments have identified the impacts of activities on marine environment.
Data collected from licensing authorities (eg. constructions, dredging) and automatic identification system (AIS) is used in an assessment of pressures by HELCOM in the Baltic Sea region. HELCOM cumulative impact assessments have identified the impacts of activities on marine environment.
Fishery is widespread activity impacting primarily target fish stocks. It also affects other fish stocks, sea-birds and marine mammals due to by-catch. In Finnish waters there are no bottom touching fishing gears in use. Fishery data is collected via EU data collection framework and catch statistics by the fishermen from the whole region.
Fishery is widespread activity impacting primarily target fish stocks. It also affects other fish stocks, sea-birds and marine mammals due to by-catch. In Finnish waters there are no bottom touching fishing gears in use. Fishery data is collected via EU data collection framework and catch statistics by the fishermen from the whole region.
Q7c - Relevant measures
Q7e - Adequacy for assessment of measures Q7d - Adequate data
Q7e - Adequacy for assessment of measures Q7d - Established methods
Q7e - Adequacy for assessment of measures Q7d - Adequate understanding of GES
Q7e - Adequacy for assessment of measures Q7d - Adequate capacity
Q7e - Adequacy for assessment of measures Q7d - Addresses activities and pressures
Q7e - Adequacy for assessment of measures Q7d - Addresses effectiveness of measures
Q7d - Description of monitoring for measures
Q7f - Gap-filling date for activities and measures
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
By2014
Q8a - Links to existing Monitoring Programmes
  • Birds
  • HELCOM
  • Habitats
  • Birds
  • HELCOM
  • Habitats
  • Birds
  • HELCOM
  • Habitats
  • Birds
  • HELCOM
  • Habitats
  • Birds
  • HELCOM
  • Habitats
  • CFP-DC-MAP
  • HELCOM
  • Habitats
  • CFP-DC-MAP
  • HELCOM
  • Habitats
  • CFP-DC-MAP
  • HELCOM
  • Habitats
  • HELCOM
  • Habitats
  • HELCOM
  • Habitats
  • HELCOM
  • Habitats
  • WFD
  • HELCOM
  • Habitats
  • WFD
  • HELCOM
  • Habitats
  • WFD
  • HELCOM
  • Habitats
  • WFD
  • CFP-DC-MAP
  • HELCOM
  • Habitats
  • CFP-DC-MAP
  • HELCOM
  • Habitats
Reference sub-programme Sub-programme ID
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-2
BALFI-D01,04,06bir-3
BALFI-D01,04,06bir-4
BALFI-D01,04,06bir-4
BALFI-D01,04,06fis-1
BALFI-D01,04,06fis-2
BALFI-D01,04,06fis-3
BALFI-D01,04,06mam-1
BALFI-D01,04,06mam-2
BALFI-D01,04,06ben-1
BALFI-D01,04,06ben-2
BALFI-D01,04,06ben-3
BALFI-D01,04,06ben-4
BALFI-D03-1
BALFI-D03-2
Reference sub-programme Sub-programme name
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - mortality/injury rates from other human activities
Mobile species - health status
Mobile species - mortality/injury rates from other human activities
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - health status
Benthic species - abundance and/or biomass
Benthic species - abundance and/or biomass
Seabed habitats - distribution and extent
Physical disturbance - from dredging and disposal of dredged material
Activities extracting living resources (fisheries including recreational, maerl, seaweed)
Activities extracting living resources (fisheries including recreational, maerl, seaweed)
Q4g - Sub-programmes Sub-programme ID
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-2
BALFI-D01,04,06bir-3
BALFI-D01,04,06bir-4
BALFI-D01,04,06bir-4
BALFI-D01,04,06fis-1
BALFI-D01,04,06fis-2
BALFI-D01,04,06fis-3
BALFI-D01,04,06mam-1
BALFI-D01,04,06mam-2
BALFI-D01,04,06ben-1
BALFI-D01,04,06ben-2
BALFI-D01,04,06ben-3
BALFI-D01,04,06ben-4
BALFI-D03-1
BALFI-D03-2
Q4g - Sub-programmes Sub-programme name
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - mortality/injury rates from other human activities
Mobile species - health status
Mobile species - mortality/injury rates from other human activities
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - abundance and/or biomass
Mobile species - health status
Benthic species - abundance and/or biomass
Benthic species - abundance and/or biomass
Seabed habitats - distribution and extent
Physical disturbance - from dredging and disposal of dredged material
Activities extracting living resources (fisheries including recreational, maerl, seaweed)
Activities extracting living resources (fisheries including recreational, maerl, seaweed)
Q4k - Monitoring purpose
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact
StateImpact Pressurse Activities
StateImpact
StateImpact
Q4l - Links of monitoring programmes of other Directives and Conventions
This sub-programme refers to the monitoring which has been reported under the Birds Directive and the Habitats Directive. Further information describing this national sub-programme is available in: HELCOM Monitoring manual - Sub-programme: Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Monitoring of marine breeding birds is not yet fully coordinated at region level.
HELCOM Monitoring manual - Sub-programme: Marine wintering birds abundance and distribution - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-wintering-birds-abundance-and-distribution Essential information describing this national sub-programme is available in the above mentioned HELCOM Monitoring manual sub-programme.
Not relevant
Essential information describing this national sub-programme is available in: HELCOM Monitoring manual - Sub-programme: Marine bird health - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health
Essential information describing this national sub-programme is available in: HELCOM Monitoring manual - Sub-programme: Marine bird health - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health
Not relevant
Essential information describing this national sub-programme is available in: HELCOM Monitoring manual - Sub-programme: Migratory fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/migratory-fish
Essential information describing this national sub-programme is available in: HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish
Essential information describing this national sub-programme is available in: HELCOM Monitoring manual - Sub-programme: Seal abundance - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/seals-abundance
Essential information describing this national sub-programme is available in: HELCOM Monitoring manual - Sub-programme: Seal health status - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/health-status
HELCOM Monitoring manual - Sub-programme: Softbottom fauna - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna HELCOM Monitoring manual - Sub-programme: Seabed habitat physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/seabed-habitat-physical-characteristics Essential information describing this national sub-programme is available in the above mentioned HELCOM Monitoring manual sub-programme.
This sub-programme also refers to the monitoring which has been reported under the Water Framework Directive (Benthic fauna). Further information describing this national sub-programme is available in: HELCOM Monitoring manual - Sub-programme: Softbottom fauna - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna HELCOM Monitoring manual - Sub-programme: Seabed habitat physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/seabed-habitat-physical-characteristics
This sub-programme refers to the monitoring which has been reported under the Water Framework Directive (Benthic fauna). Further information describing this national sub-programme is available in: HELCOM Monitoring manual - Sub-programme: Hard bottom species - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/hardbottom-species . HELCOM Monitoring manual - Sub-programme: Habitat forming species - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/habitat-forming-species-and-substrates
This sub-programme refers to the monitoring which has been reported under the Water Framework Directive.
Essential information describing this national sub-programme is available in: HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish HELCOM Monitoring manual - Sub-programme: Offshore fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish
Essential information describing this national sub-programme is available in: HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish HELCOM Monitoring manual - Sub-programme: Offshore fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish
Q5c - Features Q5c - Habitats
  • LitRock LitSed ShallRock ShallCoarseSed ShallSand ShallMud ShallMxdSed ShelfCoarseSed ShelfSand ShelfMud ShelfMxdSed
  • LitRock LitSed ShallRock ShallCoarseSed ShallSand ShallMud ShallMxdSed ShelfCoarseSed ShelfSand ShelfMud ShelfMxdSed
  • LitRock LitSed ShallRock ShallCoarseSed ShallSand ShallMud ShallMxdSed ShelfCoarseSed ShelfSand ShelfMud ShelfMxdSed
  • LitRock LitSed ShallRock ShallCoarseSed ShallSand ShallMud ShallMxdSed ShelfCoarseSed ShelfSand ShelfMud ShelfMxdSed
Q5c - Features Q5c - Species list
  • AnnexII_IV_V_Species
  • BirdsInshoreBenthic
  • BirdsInshoreHerbiv
  • BirdsInshorePelagic
  • BirdsInshoreSurface
  • BirdsIntertidalBenthic
  • BirdsOffshorePelagic
  • MammalsIce
  • MammalsSeals
  • WildBirdSpecies
  • AnnexII_IV_V_Species
  • BirdsInshoreBenthic
  • BirdsInshoreHerbiv
  • BirdsInshorePelagic
  • BirdsInshoreSurface
  • BirdsIntertidalBenthic
  • BirdsOffshorePelagic
  • MammalsIce
  • MammalsSeals
  • WildBirdSpecies
  • AnnexII_IV_V_Species
  • BirdsInshoreBenthic
  • BirdsInshoreHerbiv
  • BirdsInshorePelagic
  • BirdsInshoreSurface
  • BirdsIntertidalBenthic
  • BirdsOffshorePelagic
  • MammalsIce
  • MammalsSeals
  • WildBirdSpecies
  • AnnexII_IV_V_Species
  • BirdsInshoreBenthic
  • BirdsInshoreHerbiv
  • BirdsInshorePelagic
  • BirdsInshoreSurface
  • BirdsIntertidalBenthic
  • BirdsOffshorePelagic
  • MammalsIce
  • MammalsSeals
  • WildBirdSpecies
  • AnnexII_IV_V_Species
  • BirdsInshoreBenthic
  • BirdsInshoreHerbiv
  • BirdsInshorePelagic
  • BirdsInshoreSurface
  • BirdsIntertidalBenthic
  • BirdsOffshorePelagic
  • MammalsIce
  • MammalsSeals
  • WildBirdSpecies
  • AnnexII_IV_V_Species
  • FishCoastal
  • FishDemersal
  • FishDiadromous
  • FishPelagic
  • AnnexII_IV_V_Species
  • FishCoastal
  • FishDemersal
  • FishDiadromous
  • FishPelagic
  • AnnexII_IV_V_Species
  • FishCoastal
  • FishDemersal
  • FishDiadromous
  • FishPelagic
  • AnnexII_IV_V_Species
  • MammalsIce
  • MammalsSeals
  • MammalsToothedWhales
  • AnnexII_IV_V_Species
  • MammalsIce
  • MammalsSeals
  • MammalsToothedWhales
  • AnnexII_IV_V_Species
  • Clupea_harengus_membras_Linnaeus_1761
  • FishCoastal
  • FishDemersal
  • FishDiadromous
  • FishPelagic
  • Gadus_morhua_Linnaeus_1758
  • AnnexII_IV_V_Species
  • Clupea_harengus_membras_Linnaeus_1761
  • FishCoastal
  • FishDemersal
  • FishDiadromous
  • FishPelagic
  • Gadus_morhua_Linnaeus_1758
Q5c - Features Q5c - Physical/Chemical features
  • H2S, sediment color, substrate type
  • OxygenLevels
  • PhysicalChemicalOther
  • Salinity
  • SeaBottomTemperature
  • WaveExposure
  • H2S, sediment color, substrate type
  • OxygenLevels
  • PhysicalChemicalOther
  • Salinity
  • SeaBottomTemperature
  • WaveExposure
  • H2S, sediment color, substrate type
  • OxygenLevels
  • PhysicalChemicalOther
  • Salinity
  • SeaBottomTemperature
  • WaveExposure
  • H2S, sediment color, substrate type
  • OxygenLevels
  • PhysicalChemicalOther
  • Salinity
  • SeaBottomTemperature
  • WaveExposure
Q5c - Features Q5c - Pressures
  • ExtractSpeciesOther
  • hunting of seals and seabirds
  • ExtractSpeciesOther
  • hunting of seals and seabirds
  • ExtractSpeciesOther
  • hunting of seals and seabirds
  • ExtractSpeciesOther
  • hunting of seals and seabirds
  • ExtractSpeciesOther
  • hunting of seals and seabirds
  • Bycatch
  • PressureOther
  • Bycatch
  • PressureOther
  • PhysDam
  • PhysDam_abrasion
  • PhysDam_extraction
  • PhysDam_silt
  • PhysDisturbance
  • PhysLoss
  • PhysLoss_Seal
  • PhysLoss_Smother
  • PhysDam
  • PhysDam_abrasion
  • PhysDam_extraction
  • PhysDam_silt
  • PhysDisturbance
  • PhysLoss
  • PhysLoss_Seal
  • PhysLoss_Smother
  • PhysDam
  • PhysDam_abrasion
  • PhysDam_extraction
  • PhysDam_silt
  • PhysDisturbance
  • PhysLoss
  • PhysLoss_Seal
  • PhysLoss_Smother
  • PhysDam
  • PhysDam_abrasion
  • PhysDam_extraction
  • PhysDam_silt
  • PhysDisturbance
  • PhysLoss
  • PhysLoss_Seal
  • PhysLoss_Smother
  • ExtractSpeciesFishShellfish
  • ExtractSpeciesFishShellfish
Q9a - Elements
  • marine breeding birds
  • marine birds
  • Marine birds
  • Haliaetus_albicilla_Linnaeus_1758
  • Haliaetus_albicilla_Linnaeus_1758
  • Coregonus_lavaretus_Linnaeus_1758
  • Diadromous fish
  • Salmo_trutta_trutta_Linnaeus_1758
  • coastal fish
  • Halichoerus_grypus_Fabricius_1791
  • Phocoena_phocoena_Linnaeus_1758
  • Pusa_hispida_bottnica_Schreber_1775
  • marine seals
  • littoral sediment
  • macrozoobenthos
  • shelf sublittoral coarse sediment
  • shelf sublittoral mixed sediment
  • shelf sublittoral mud
  • shelf sublittoral sand
  • littoral sediment
  • macrozoobenthos
  • shallow sublittoral coarse sediment
  • shallow sublittoral mixed sediment
  • shallow sublittoral mud
  • shallow sublittoral sand
  • Blue mussel
  • Littoral rock and biogenic reef
  • Macroalgae
  • Macrozoobenthos
  • Shallow sublittoral rock and biogenic reef
  • contaminant levels in dredged material
  • disposal of dredged matter
  • dredging
  • marine constructions
  • selective exploitation of the seabed
  • shipping
  • Clupea_harengus_Linnaeus_1761
  • Gadus_morhua_Linnaeus_1758
  • Salmo_salar_Linnaeus_1758
  • Sprattus sprattus_Linnaeus_1758
  • coastal fish
  • commercial fish stocks
Q5a - GES criteria Relevant GES criteria
  • 1.1
  • 1.2
  • 1.3
  • 4.1
  • 4.2
  • 4.3
  • 8.2
  • 1.1
  • 1.2
  • 1.3
  • 4.1
  • 4.2
  • 4.3
  • 8.2
  • 1.1
  • 1.2
  • 1.3
  • 4.1
  • 4.2
  • 4.3
  • 8.2
  • 1.1
  • 1.2
  • 1.3
  • 4.1
  • 4.2
  • 4.3
  • 8.2
  • 1.1
  • 1.2
  • 1.3
  • 4.1
  • 4.2
  • 4.3
  • 8.2
  • 1.2
  • 1.3
  • 3.2
  • 3.3
  • 4.3
  • 1.2
  • 1.3
  • 3.2
  • 3.3
  • 4.3
  • 1.2
  • 1.3
  • 3.2
  • 3.3
  • 4.3
  • 1.1
  • 1.2
  • 1.3
  • 4.1
  • 4.2
  • 4.3
  • 8.2
  • 1.1
  • 1.2
  • 1.3
  • 4.1
  • 4.2
  • 4.3
  • 8.2
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 1.6
  • 4.3
  • 5.3
  • 6.1
  • 6.2
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 1.6
  • 4.3
  • 5.3
  • 6.1
  • 6.2
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 1.6
  • 4.3
  • 5.3
  • 6.1
  • 6.2
  • 1.1
  • 1.2
  • 1.3
  • 1.4
  • 1.5
  • 1.6
  • 4.3
  • 5.3
  • 6.1
  • 6.2
  • 1.1
  • 1.2
  • 1.3
  • 3.1
  • 3.2
  • 3.3
  • 1.1
  • 1.2
  • 1.3
  • 3.1
  • 3.2
  • 3.3
Q5b - GES indicators Relevant GES indicators
  • 1.1.1
  • 1.1.2
  • 1.2.1
  • 4.1.1
  • 4.3.1
  • 8.2.1
  • 1.1.1
  • 1.1.2
  • 1.2.1
  • 4.1.1
  • 4.3.1
  • 8.2.1
  • 1.1.1
  • 1.1.2
  • 1.2.1
  • 4.1.1
  • 4.3.1
  • 8.2.1
  • 1.1.1
  • 1.1.2
  • 1.2.1
  • 4.1.1
  • 4.3.1
  • 8.2.1
  • 1.1.1
  • 1.1.2
  • 1.2.1
  • 4.1.1
  • 4.3.1
  • 8.2.1
  • 1.2.1
  • 1.3.1
  • 3.1.2
  • 3.2.2
  • 3.3.1
  • 3.3.2
  • 3.3.4
  • 4.3.1
  • 1.2.1
  • 1.3.1
  • 3.1.2
  • 3.2.2
  • 3.3.1
  • 3.3.2
  • 3.3.4
  • 4.3.1
  • 1.2.1
  • 1.3.1
  • 3.1.2
  • 3.2.2
  • 3.3.1
  • 3.3.2
  • 3.3.4
  • 4.3.1
  • 1.1.1
  • 1.1.2
  • 1.2.1
  • 1.3.1
  • 4.1.1
  • 4.3.1
  • 8.2.1
  • 1.1.1
  • 1.1.2
  • 1.2.1
  • 1.3.1
  • 4.1.1
  • 4.3.1
  • 8.2.1
  • 1.4.1
  • 1.4.2
  • 1.5.1
  • 1.5.2
  • 1.6.1
  • 1.6.2
  • 1.6.3
  • 4.3.1
  • 5.3.1
  • 6.1.1
  • 6.1.2
  • 6.2.2
  • 6.2.3
  • 1.4.1
  • 1.4.2
  • 1.5.1
  • 1.5.2
  • 1.6.1
  • 1.6.2
  • 1.6.3
  • 4.3.1
  • 5.3.1
  • 6.1.1
  • 6.1.2
  • 6.2.2
  • 6.2.3
  • 1.4.1
  • 1.4.2
  • 1.5.1
  • 1.5.2
  • 1.6.1
  • 1.6.2
  • 1.6.3
  • 4.3.1
  • 5.3.1
  • 6.1.1
  • 6.1.2
  • 6.2.2
  • 6.2.3
  • 1.4.1
  • 1.4.2
  • 1.5.1
  • 1.5.2
  • 1.6.1
  • 1.6.2
  • 1.6.3
  • 4.3.1
  • 5.3.1
  • 6.1.1
  • 6.1.2
  • 6.2.2
  • 6.2.3
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 3.1.1
  • 3.1.2
  • 3.2.1
  • 3.2.2
  • 1.1.1
  • 1.2.1
  • 1.3.1
  • 3.1.1
  • 3.1.2
  • 3.2.1
  • 3.2.2
Q9b - Parameters monitored (state/impact) Species distribution
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-1
  • MP-9b-1-1-1
Q9b - Parameters monitored (state/impact) Species population size
  • MP-9b-1-2-1
  • MP-9b-1-2-1
  • MP-9b-1-2-1
  • MP-9b-1-2-1
  • MP-9b-1-2-1
  • MP-9b-1-2-1
  • MP-9b-1-2-2
  • MP-9b-1-2-1
  • MP-9b-1-2-1
  • MP-9b-1-2-1
  • MP-9b-1-2-1
  • MP-9b-1-2-1
Q9b - Parameters monitored (state/impact) Species population characteristics
  • MP-9b-1-3-8
  • MP-9b-1-3-5
  • MP-9b-1-3-6
  • MP-9b-1-3-7
  • MP-9b-1-3-8
  • MP-9b-1-3-5
  • MP-9b-1-3-6
  • MP-9b-1-3-7
  • MP-9b-1-3-8
  • MP-9b-1-3-1
  • MP-9b-1-3-2
  • MP-9b-1-3-5
  • MP-9b-1-3-1
  • MP-9b-1-3-5
  • MP-9b-1-3-5
  • MP-9b-1-3-6
  • MP-9b-1-3-7
  • MP-9b-1-3-2
  • MP-9b-1-3-3
  • MP-9b-1-3-6
  • MP-9b-1-3-7
  • MP-9b-1-3-6
  • MP-9b-1-3-7
  • MP-9b-1-3-8
  • MP-9b-1-3-5
Q9b - Parameters monitored (state/impact) Species impacts
  • MP-9b-1-4-4
Q9b - Parameters monitored (state/impact) Habitat distribution
  • MP-9b-1-5-1
  • MP-9b-1-5-1
  • MP-9b-1-5-1
Q9b - Parameters monitored (state/impact) Habitat extent
  • MP-9b-1-6-1
  • MP-9b-1-6-1
  • MP-9b-1-6-1
Q9b - Parameters monitored (state/impact) Habitat condition (physical-chemical)
  • MP-9b-1-7-12
  • MP-9b-1-7-13
  • MP-9b-1-7-6
  • MP-9b-1-7-12
  • MP-9b-1-7-13
  • MP-9b-1-7-6
  • MP-9b-1-7-12
  • MP-9b-1-7-13
  • MP-9b-1-7-5
  • MP-9b-1-7-12
Q9b - Parameters monitored (state/impact) Habitat condition (biological)
  • MP-9b-1-8-1
  • MP-9b-1-8-2
  • MP-9b-1-8-3
  • MP-9b-1-8-1
  • MP-9b-1-8-2
  • MP-9b-1-8-3
  • MP-9b-1-8-1
  • MP-9b-1-8-2
  • MP-9b-1-8-5
  • MP-9b-1-8-6
  • MP-9b-1-8-1
  • MP-9b-1-8-2
Q9b - Parameters monitored (state/impact) Habitat impacts
  • MP-9b-1-9-1
Q9b - Parameters monitored (pressures) Pressure input
  • MP-9b-2-1-3
Q9b - Parameters monitored (pressures) Pressure output
  • MP-9b-2-2-4
Q9b - Parameters monitored (activity) Activity
  • MP-9b-3-1-4
  • MP-9b-3-1-4
Q9b Parameters monitored (other) Other
Q41 Spatial scope
WFD_CW
WFD_CW TerritorialWaters
WFD_CW TerritorialWaters
WFD_CW TerritorialWaters
WFD_CW TerritorialWaters
WFD_CW
WFD_TW
WFD_CW
WFD_CW TerritorialWaters EEZ
WFD_CW TerritorialWaters EEZ
TerritorialWaters BeyondMSwaters
WFD_CW TerritorialWaters
WFD_CW
WFD_CW TerritorialWaters EEZ
WFD_CW TerritorialWaters EEZ BeyondMSwaters
WFD_CW TerritorialWaters EEZ BeyondMSwaters
Q4j - Description of spatial scope
HELCOM Monitoring manual - Sub-programme: Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 43 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
HELCOM Monitoring manual - Sub-programme: Marine wintering birds abundance and distribution - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-wintering-birds-abundance-and-distribution
Mass mortalities of breeding sea birds are monitored in the vicinity of breeding colonies. Therefore the monitoring is focuses on islands and islets in coastal and territorial waters.
HELCOM Monitoring manual - Sub-programme: Marine bird health - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health
HELCOM Monitoring manual - Sub-programme: Marine bird health - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health
The sub-programme monitors in the sea the structure of the river-spawning White Fish populations, which migrate to spawn in the rivers of the Bothnian Bay.
HELCOM Monitoring manual - Sub-programme: Migratory fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/migratory-fish
HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish
HELCOM Monitoring manual - Sub-programme: Seal abundance - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/seals-abundance
HELCOM Monitoring manual - Sub-programme: Seal health status - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/health-status
HELCOM Monitoring manual - Sub-programme: Softbottom fauna - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna
HELCOM Monitoring manual - Sub-programme: Softbottom fauna - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna
HELCOM Monitoring manual - Sub-programme: Hard bottom species - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/hardbottom-species . HELCOM Monitoring manual - Sub-programme: Habitat forming species - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/habitat-forming-species-and-substrates
Siltation, dredging and selective exploitation of seabed is carried out in the coastal areas of all Finnish marine sub-basins.
HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish HELCOM Monitoring manual - Sub-programme: Offshore fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish
HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish HELCOM Monitoring manual - Sub-programme: Offshore fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish
Marine Unit IDs
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
  • BAL-FI-RG-Baltic Sea
Q4h - Temporal scope Start date- End date
1948-9999
1965-9999
1986-9999
1970-9999
1970-9999
1980-9999
1976-9999
1970-9999
1988-9999
1977-9999
1965-9999
1965-9999
2006-9999
2014-9999
1970-9999
1970-9999
Q9h - Temporal resolution of sampling
  • Yearly
  • Yearly
  • Asneeded
  • Yearly
  • Yearly
  • 2-3 times per spawning season
  • Other
  • Yearly
  • Yearly
  • Yearly
  • Unknown
  • Yearly
  • Yearly
  • Yearly
  • 6yearly
  • Unknown
  • Unknown
Q9c - Monitoring method
HELCOM Monitoring manual - Sub-programme: Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 43 selected breeding areas situated along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
HELCOM Monitoring manual - Sub-programme: Marine wintering birds abundance and distribution - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-wintering-birds-abundance-and-distribution
The frequency of mortality events and the number of dead seabird species are recorded
HELCOM Monitoring manual - Sub-programme: Marine bird health - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health
HELCOM Monitoring manual - Sub-programme: Marine bird health - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health
Spawning Whitefish, migrating to rivers in September-October, are sampled from catches caught by local fishermen. Various fishing gear are used (e.g. net and fyke) to catch a few hundred individuals per river. The samplings take place 2-3 times during each spawning season.
Sea trout parr are caught by electro fishing, after which they are tagged and released. HELCOM Monitoring manual - Sub-programme: Migratory fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/migratory-fish
HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish
HELCOM Monitoring manual - Sub-programme: Seal abundance - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/seals-abundance
HELCOM Monitoring manual - Sub-programme: Seal health status - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/health-status
HELCOM Monitoring manual - Sub-programme: Softbottom fauna - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna HELCOM Monitoring manual - Sub-programme: Seabed habitat physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/seabed-habitat-physical-characteristics Essential information describing this national sub-programme is available in the above mentioned HELCOM Monitoring manual sub-programme.
HELCOM Monitoring manual - Sub-programme: Softbottom fauna - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna HELCOM Monitoring manual - Sub-programme: Seabed habitat physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/seabed-habitat-physical-characteristics Essential information describing this national sub-programme is available in the above mentioned HELCOM Monitoring manual sub-programme.
HELCOM Monitoring manual - Sub-programme: Hard bottom species - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/hardbottom-species . HELCOM Monitoring manual - Sub-programme: Habitat forming species - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/habitat-forming-species-and-substrates HELCOM Combine manual. Annex C-9 Guidelines for monitoring of phytobenthic plant and animal communities in the Baltic Sea http://www.helcom.fi/stc/files/CombineManual/PartC/AnnexC9.pdf
The level of contaminants (Hg, Cd, Cu, PAH, PCB, TBT) and the volume of dredged masses are measured as a part of monitoring of licensed activities along the Finnish coast. The volume of dredged masses are measured and the contaminant levels are determined by standard methods.The cumulative effects of selective exploitation of the seabed is also monitored within this sub-programme. Information on marine constructions and shipping is collected through licensing authorities and HELCOM.
HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish HELCOM Monitoring manual - Sub-programme: Offshore fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish
HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish HELCOM Monitoring manual - Sub-programme: Offshore fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish
Q9d - Description of alteration to method
Finland carries out all monitoring of seals by surveys from air crafts. Finland records occasional observations of Harbour Porposes to a HELCOM database (http://www.helcom.fi/baltic-sea-trends/data-maps/habitat/harbour-porpoise/)
Monitoring of shallow seabed habitats has been started in the Finnish underwater mapping program VELMU. The VELMU-program provides baseline habitat maps for the basis of future monitoring. The monitoring methods are described in the HELCOM Monitoring manual (see above).
Q9e - Quality assurance
  • COMBINE
  • National
  • standard defined by Finnish experts
  • National
  • standard defined by Finnsih experts
  • Unknown
  • COMBINE
  • COMBINE
  • Unknown
  • Unknown
  • COMBINE
  • COMBINE
  • National
  • Unknown
  • COMBINE
  • COMBINE
  • COMBINE
  • Contamination: National. Dredging: HELCOM. Construction: EIA legislation
  • Other
  • COMBINE
  • ICESDataTypeGuide
  • COMBINE
  • ICESDataTypeGuide
Q9f - Quality control
RealandDelayedValidation
RealandDelayedValidation
Unknown
RealandDelayedValidation
RealandDelayedValidation
Unknown
Unknown
RealValidation
RealandDelayedValidation
Unknown
RealandDelayedValidation
RealandDelayedValidation
RealandDelayedValidation
Unknown
Unknown
Unknown
Q9g - Spatial resolution of sampling Q9g - Proportion of area covered %
100
100
15
100
100
100
Q9g - Spatial resolution of sampling Q9g - No. of samples
HELCOM Monitoring manual - Sub-programme: Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/
HELCOM Monitoring manual - Sub-programme: Marine wintering birds abundance and distribution - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-wintering-birds-abundance-and-distribution
Observations made by the public and by the birding people are collected from the whole Finnish coastal and open sea area (Aland islands included). The bird monitoring observation network includes several important Razorbill- and tern colonies.
HELCOM Monitoring manual - Sub-programme: Marine bird health - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health
HELCOM Monitoring manual - Sub-programme: Marine bird health - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health
Eight rivers in the Bothnian Bay.
HELCOM Monitoring manual - Sub-programme: Migratory fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/migratory-fish
HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish
HELCOM Monitoring manual - Sub-programme: Seal abundance - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/seals-abundance
HELCOM Monitoring manual - Sub-programme: Seal health status - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/health-status
HELCOM Monitoring manual - Sub-programme: Softbottom fauna - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna . HELCOM Monitoring manual - Sub-programme: Seabed habitat physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/seabed-habitat-physical-characteristics
HELCOM Monitoring manual - Sub-programme: Softbottom fauna - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna . HELCOM Monitoring manual - Sub-programme: Seabed habitat physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/seabed-habitat-physical-characteristics
HELCOM Monitoring manual - Sub-programme: Hard bottom species - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/hardbottom-species . HELCOM Monitoring manual - Sub-programme: Habitat forming species - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/seabed-habitat-distribution-and-extent/habitat-forming-species-and-substrates . HELCOM Combine manual. Annex C-9 Guidelines for monitoring of phytobenthic plant and animal communities in the Baltic Sea http://www.helcom.fi/stc/files/CombineManual/PartC/AnnexC9.pdf
Monitoring of all activities is done in all Finnish coastal areas (all sub-basins).
HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish HELCOM Monitoring manual - Sub-programme: Offshore fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish
HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish HELCOM Monitoring manual - Sub-programme: Offshore fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish
Q9i - Description of sample representivity
Information on the following activities is collected at HELCOM level: RenewableEnergy, MiningSandGravel, Dredging, Ports, CablesPipelines, OffshoreStructures, Shipping and SolidWasteDisposal. See under "Action areas" at: http://www.helcom.fi/action-areas
Information on the activity Fisheries is collected at HELCOM level. See under "Action areas" at: http://www.helcom.fi/action-areas
Q10a - Scale for aggregation of data
  • Other
  • Region
  • national marine areas;
  • Region
  • National
  • Other
  • Region
  • Region
  • Bothnian Bay
  • Other
  • Region
  • Region
  • Region
  • Region
  • Region
  • Region
  • Region
  • Region
  • Region
  • Region
Q10b - Other scale for aggregation of data
Because the Baltic sea bird individuals belong to the same population, co-operation between the HELCOM states would be important. However, only a little co-operation has occurred in the Baltic Sea region so far .
Neighboring countries do not have this sub-programme
The only significant river spawning White Fish populations occur in the Bothnian Bay
Q10c - Access to monitoring data Q10c - Data type
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData DataProducts
ProcessedData DataProducts
Q10c - Access to monitoring data Q10c - Data access mechanism
LocationNationalDC
URLview
URLview
URLview
URLview
URLview
URLview
URLview
URLview
URLview
URLview
URLview
URLview
URLview
URLview
URLview
Q10c - Access to monitoring data Q10c - Data access rights
RestrictedGeneral
Open
Open
Open
Open
Open
Open
Open
Open
Open
Open
Open
Open
Open
Open
Open
Q10c - Access to monitoring data Q10c - INSPIRE standard
SeaRegions SpeciesDistribution
SeaRegions SpeciesDistribution
SeaRegions SpeciesDistribution
SeaRegions SpeciesDistribution
SeaRegions SpeciesDistribution
SeaRegions SpeciesDistribution
SpeciesDistribution
SeaRegions SpeciesDistribution
SeaRegions SpeciesDistribution
SeaRegions SpeciesDistribution
SeaRegions SpeciesDistribution
SeaRegions SpeciesDistribution
HabitatsBiotopes SpeciesDistribution
Geology HabitatsBiotopes SpeciesDistribution
SpeciesDistribution
SpeciesDistribution
Q10c - Access to monitoring data Q10c Date data are available
2015-12
2015-12
2015-12
2015-12
2015-12
2015-12
2015-12
2015-12
2015-12
2015-12
2015-12
2015-12
2015-12
2015-12
2015-12
2015-12
Q10c - Access to monitoring data Q10c - Data update frequency
Yearly
Yearly
Asneeded
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
6yearly
Yearly
Yearly
Q10d - Description of data access
HELCOM CORE indicator - Abundance of waterbirds in the wintering season​: http://www.helcom.fi/baltic-sea-trends/biodiversity/indicators/abundance-of-waterbirds-in-the-wintering-season/ Data is also available upon request from the Finnish Museum of Natural History (LUOMUS) - http://www.luomus.fi/en/species-distribution-and-biogeography A summary showing the occurrence of breeding birds by species (based on the "Third Finnish Breeding Bird Atlas") is available at: http://atlas3.lintuatlas.fi/results/specieslist
HELCOM CORE indicator - Abundance of waterbirds in the wintering season​: http://www.helcom.fi/baltic-sea-trends/biodiversity/indicators/abundance-of-waterbirds-in-the-wintering-season/ Essential information on data access is available in the HELCOM Monitoring manual - Sub-programme: Marine wintering birds abundance and distribution - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-wintering-birds-abundance-and-distribution
By request
HELCOM CORE indicator - MARINE BIRD HEALTH: http://www.helcom.fi/baltic-sea-trends/biodiversity/indicators/white-tailed-eagle-productivity/ Essential information on data access is available in the HELCOM Monitoring manual - Sub-programme: Marine bird health - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health
HELCOM CORE indicator - MARINE BIRD HEALTH: http://www.helcom.fi/baltic-sea-trends/biodiversity/indicators/white-tailed-eagle-productivity/ Essential information on data access is available in the HELCOM Monitoring manual - Sub-programme: Marine bird health - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-bird-health
Data available by request from the Finnish Game and Fisheries Research Institute - http://www.rktl.fi/english/fish/fish_resources/whitefish_in_the_1.html
HELCOM CORE indicator - Abundance of Sea Trout spawners and parr - http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Abundance_of_sea_trout_spawners_and_parr.pdf Data on tagged fish is available by request from Finnish Game and Fisheries Research Institute - http://www.rktl.fi/english/fish/fish_resources/ OIVA-open data service (in Finnish): https://wwwp2.ymparisto.fi/scripts/oiva.asp More information on data access is available in the HELCOM Monitoring manual - Sub-programme: Migratory fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/migratory-fish
HELCOM CORE indicator - Abundance of key fish species - http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Abundance_of_key_fish_species.pdf HELCOM CORE indicator - Abundance of fish key functional groups - http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Abundance_of_fish_key_functional_groups.pdf Public web service on environmental information OIVA (in Finnish) - www.ymparisto.fi/oiva More information on data access is available in the HELCOM Monitoring manual - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish
HELCOM CORE indicator - http://helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Population_growth_rate_abundance_and_distribution_of_marine_mammals.pdf Essential information on data access is available in the HELCOM Monitoring manual - Sub-programme: Seal abundance - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/seals-abundance
HELCOM CORE indicator - Pregnancy rates of the marine mammals-Particular emphasis on Baltic grey and ringed seals: http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Pregnancy_rates_of_marine_mammals.pdf HELCOM CORE indicator - Nutritional status of seals: http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Nutritional_status_of_seals.pdf Essential information about data access is available in the HELCOM Monitoring manual - Sub-programme: Seal health status - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/health-status
HELCOM CORE indicator - State of the soft-bottom macrofauna communities - http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator_State_of_the_soft-bottom_macrofauna_communities.pdf OIVA public web portal on environmental information (in Finnish) - www.ymparisto.fi/oiva OIVA is linked to the Finnish benthos database POHJE Essential information on data access is available in the HELCOM Monitoring manual - Sub-programme: Softbottom fauna - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna
HELCOM CORE indicator - State of the soft-bottom macrofauna communities - http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator_State_of_the_soft-bottom_macrofauna_communities.pdf OIVA public web portal on environmental information (in Finnish) - www.ymparisto.fi/oiva OIVA is linked to the Finnish benthos database POHJE Essential information on data access is available in the HELCOM Monitoring manual - Sub-programme: Softbottom fauna - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna
HELCOM CORE indicator - Population structure of long-lived macrozoobenthic species http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator_Population_structure_of_long-lived_macrozoobenthic_species.pdf OIVA public web portal on environmental information (in Finnish) - http://www.ymparisto.fi/oiva OIVA is linked to the Finnish benthos database POHJE Essential information on data access is available in the HELCOM Monitoring manual: Sub-programme: Hard bottom species - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/hardbottom-species (NOT COORDINATED) Sub-programme: Soft bottom flora - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-flora
OIVA public web portal on environmental information (in Finnish) - http://www.ymparisto.fi/oiva
HELCOM CORE Indicator: Abundance of key fish species - http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Abundance_of_key_fish_species.pdf HELCOM CORE Indicator: Proportion of large fish in the community - http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Proportion_of_large_fish_in_the_community.pdf Essential information on data access is available in the HELCOM Monitoring manual: - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish - Sub-programme: Offshore fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish
HELCOM CORE Indicator: Abundance of key fish species - http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Abundance_of_key_fish_species.pdf HELCOM CORE Indicator: Proportion of large fish in the community - http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Proportion_of_large_fish_in_the_community.pdf Essential information on data access is available in the HELCOM Monitoring manual: - Sub-programme: Coastal fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/coastal-fish - Sub-programme: Offshore fish - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/fish-fisheries-and-shellfish/offshore-fish
Descriptor
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
D1.1
Monitoring strategy description
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
The sub-programmes provide information on the size and distribution of seabird breeding populations, the number and occurrence of wintering waterbirds, the possible occurrence of mass deaths of seabirds, the production of marine eagle and the number of seabirds hunted. The hunting catch sub-programme also collects data on hunted seals. From a long-term perspective, the status of seabird populations in the Baltic Sea has been influenced by the release of oil, the accumulation of environmental poisons, the spread of which into the archipelago, the previous collection of eggs, the death of birds in fishing gear and hunting. The conditions in the breeding or wintering areas outside the Baltic Sea also affect the numbers of birds in the Baltic Sea. Global warming has an impact on the ice situation in the Baltic Sea, which contributes to the distribution of wintering waterfowl. The programme provides data for descriptors 1 (criteria D1C1, D1C2 and D1C), 4 (criteria D4C1 and D4C3) and 8 (criteria D8C2). Data on the numbers of seabirds dying in fishing gear have not been systematically collected in Finland in the past, but since 2013 commercial fisheries catch reporting forms have also been requested to fill in data on birds killed in fishing gear (see sub-programme Commercial catch statistics). In practice, seabirds of the same species in the Baltic Sea belonged to the same population, so it would be justified to combine the results of different coastal States in order to produce reliable and comprehensive farm assessments.
Coverage of GES criteria
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Gaps and plans
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
No gaps.
Related targets
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
  • LUONTO5
  • LUVA3
  • LUVAyleinen
Coverage of targets
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Related measures
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
  • BALFI-M025-HABIT - 'HABIT1 - Improve conservation in marine protected areas'
  • BALFI-M026-HABIT - 'HABIT2 - Action plans for endangered species and habitats'
Coverage of measures
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Related monitoring programmes
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
  • 04
  • 06bir-1
  • 06bir-2
  • 06bir-3
  • 06bir-4
  • 06bir-5
  • BALFI-d01
  • BALFI-d03-2
Programme code
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-1
BALFI-D01,04,06bir-2
BALFI-D01,04,06bir-2
BALFI-D01,04,06bir-2
BALFI-D01,04,06bir-2
BALFI-D01,04,06bir-2
BALFI-D01,04,06bir-2
BALFI-D01,04,06bir-2
BALFI-D01,04,06bir-2
BALFI-D01,04,06bir-4
BALFI-D01,04,06bir-4
BALFI-D01,04,06bir-4
BALFI-D01,04,06bir-4
BALFI-D03-2
BALFI-D03-2
BALFI-D03-2
BALFI-D03-2
BALFI-D03-2
BALFI-D03-2
BALFI-D03-2
BALFI-D03-2
BALFI-D03-2
BALFI-D03-2
BALFI-D03-2
BALFI-d01,04,06bir-3
BALFI-d01,04,06bir-3
BALFI-d01,04,06bir-5
BALFI-d01,04,06bir-5
BALFI-d01,04,06bir-5
BALFI-d01,04,06bir-5
Programme name
Marine breeding birds
Marine breeding birds
Marine breeding birds
Marine breeding birds
Marine breeding birds
Marine breeding birds
Marine breeding birds
Marine breeding birds
Marine breeding birds
Marine breeding birds
Marine breeding birds
Marine wintering birds
Marine wintering birds
Marine wintering birds
Marine wintering birds
Marine wintering birds
Marine wintering birds
Marine wintering birds
Marine wintering birds
White tailed eagle breeding success
White tailed eagle breeding success
White tailed eagle breeding success
White tailed eagle breeding success
Commercial fisheries catch statistics
Commercial fisheries catch statistics
Commercial fisheries catch statistics
Commercial fisheries catch statistics
Commercial fisheries catch statistics
Commercial fisheries catch statistics
Commercial fisheries catch statistics
Commercial fisheries catch statistics
Commercial fisheries catch statistics
Commercial fisheries catch statistics
Commercial fisheries catch statistics
Mass mortalities of breeding sea birds
Mass mortalities of breeding sea birds
Hunting of sea birds and seals
Hunting of sea birds and seals
Hunting of sea birds and seals
Hunting of sea birds and seals
Update type
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Old programme codes
Programme description
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Currently the marine breeding birds counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Wintering birds monitoring and data collection on species numbers, abundance and distribution.Work cordinated by HELCOM in Baltic Sea area.
Wintering birds monitoring and data collection on species numbers, abundance and distribution.Work cordinated by HELCOM in Baltic Sea area.
Wintering birds monitoring and data collection on species numbers, abundance and distribution.Work cordinated by HELCOM in Baltic Sea area.
Wintering birds monitoring and data collection on species numbers, abundance and distribution.Work cordinated by HELCOM in Baltic Sea area.
Wintering birds monitoring and data collection on species numbers, abundance and distribution.Work cordinated by HELCOM in Baltic Sea area.
Wintering birds monitoring and data collection on species numbers, abundance and distribution.Work cordinated by HELCOM in Baltic Sea area.
Wintering birds monitoring and data collection on species numbers, abundance and distribution.Work cordinated by HELCOM in Baltic Sea area.
Wintering birds monitoring and data collection on species numbers, abundance and distribution.Work cordinated by HELCOM in Baltic Sea area.
White tailed eagle breeding success monitoring is largely based on volunteers coordinated by Sääksisäätiö-nonprofit organisation
White tailed eagle breeding success monitoring is largely based on volunteers coordinated by Sääksisäätiö-nonprofit organisation
White tailed eagle breeding success monitoring is largely based on volunteers coordinated by Sääksisäätiö-nonprofit organisation
White tailed eagle breeding success monitoring is largely based on volunteers coordinated by Sääksisäätiö-nonprofit organisation
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
Mass mortalities of breeding sea birds are monitored in the vicinity of breeding colonies. Therefore the monitoring is focuses on islands and islets in coastal and territorial waters. Aim is to register number of mass mortality's and causes
Mass mortalities of breeding sea birds are monitored in the vicinity of breeding colonies. Therefore the monitoring is focuses on islands and islets in coastal and territorial waters. Aim is to register number of mass mortality's and causes
Hunting of sea birds and seals is practiced in coastal and territorial waters according to hunting regulations.Hunting organizations carry out game questionnaires. Hunting statistics are maintained by the hunting organizations and stored into a database. Data on species requiring special permit is obtained through the licensing system.
Hunting of sea birds and seals is practiced in coastal and territorial waters according to hunting regulations.Hunting organizations carry out game questionnaires. Hunting statistics are maintained by the hunting organizations and stored into a database. Data on species requiring special permit is obtained through the licensing system.
Hunting of sea birds and seals is practiced in coastal and territorial waters according to hunting regulations.Hunting organizations carry out game questionnaires. Hunting statistics are maintained by the hunting organizations and stored into a database. Data on species requiring special permit is obtained through the licensing system.
Hunting of sea birds and seals is practiced in coastal and territorial waters according to hunting regulations.Hunting organizations carry out game questionnaires. Hunting statistics are maintained by the hunting organizations and stored into a database. Data on species requiring special permit is obtained through the licensing system.
Monitoring purpose
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Environmental state and impacts
  • Environmental state and impacts
  • Human activities causing the pressures
  • Human activities causing the pressures
  • Human activities causing the pressures
  • Human activities causing the pressures
Other policies and conventions
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • HELCOM Monitoring programmes
  • Habitats Directive
  • AEWA
  • Birds Directive
  • HELCOM Monitoring programmes
  • AEWA
  • Birds Directive
  • HELCOM Monitoring programmes
  • AEWA
  • Birds Directive
  • HELCOM Monitoring programmes
  • AEWA
  • Birds Directive
  • HELCOM Monitoring programmes
  • AEWA
  • Birds Directive
  • HELCOM Monitoring programmes
  • AEWA
  • Birds Directive
  • HELCOM Monitoring programmes
  • AEWA
  • Birds Directive
  • HELCOM Monitoring programmes
  • AEWA
  • Birds Directive
  • HELCOM Monitoring programmes
  • Birds Directive
  • HELCOM Monitoring programmes
  • Birds Directive
  • HELCOM Monitoring programmes
  • Birds Directive
  • HELCOM Monitoring programmes
  • Birds Directive
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Birds Directive
  • Birds Directive
  • Birds Directive
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
  • Birds Directive
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • HELCOM Monitoring programmes
  • Habitats Directive
Regional cooperation - coordinating body
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
  • HELCOM
  • Other
Regional cooperation - countries involved
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
DE,DK,EE,LT,LV,PL,SE
Regional cooperation - implementation level
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Monitoring details
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. — Live Yearbook 2010: 40-51
Methods for flight monitoring are agreed upon by Baltic sea countries on HELCOM (HELCOM 2015). Coastal monitoring is carried out by onshore observers. Offshore monitoring is carried out by boat and airplane.
Methods for flight monitoring are agreed upon by Baltic sea countries on HELCOM (HELCOM 2015). Coastal monitoring is carried out by onshore observers. Offshore monitoring is carried out by boat and airplane.
Methods for flight monitoring are agreed upon by Baltic sea countries on HELCOM (HELCOM 2015). Coastal monitoring is carried out by onshore observers. Offshore monitoring is carried out by boat and airplane.
Methods for flight monitoring are agreed upon by Baltic sea countries on HELCOM (HELCOM 2015). Coastal monitoring is carried out by onshore observers. Offshore monitoring is carried out by boat and airplane.
Methods for flight monitoring are agreed upon by Baltic sea countries on HELCOM (HELCOM 2015). Coastal monitoring is carried out by onshore observers. Offshore monitoring is carried out by boat and airplane.
Methods for flight monitoring are agreed upon by Baltic sea countries on HELCOM (HELCOM 2015). Coastal monitoring is carried out by onshore observers. Offshore monitoring is carried out by boat and airplane.
Methods for flight monitoring are agreed upon by Baltic sea countries on HELCOM (HELCOM 2015). Coastal monitoring is carried out by onshore observers. Offshore monitoring is carried out by boat and airplane.
Methods for flight monitoring are agreed upon by Baltic sea countries on HELCOM (HELCOM 2015). Coastal monitoring is carried out by onshore observers. Offshore monitoring is carried out by boat and airplane.
https://helcom.fi/wp-content/uploads/2019/12/Birds-Marine-bird-health.pdf
https://helcom.fi/wp-content/uploads/2019/12/Birds-Marine-bird-health.pdf
https://helcom.fi/wp-content/uploads/2019/12/Birds-Marine-bird-health.pdf
https://helcom.fi/wp-content/uploads/2019/12/Birds-Marine-bird-health.pdf
Fishermens’ reporting to authorities.
Fishermens’ reporting to authorities.
Fishermens’ reporting to authorities.
Fishermens’ reporting to authorities.
Fishermens’ reporting to authorities.
Fishermens’ reporting to authorities.
Fishermens’ reporting to authorities.
Fishermens’ reporting to authorities.
Fishermens’ reporting to authorities.
Fishermens’ reporting to authorities.
Fishermens’ reporting to authorities.
The sub-programme collects data on mass deaths of seabirds. Information can be obtained from different clubs and other sources of information, in particular public and amateur observations. The aim is to identify the number of mass deaths of seabirds and to identify the causes of death. This is, as a general rule, “passive” monitoring, i.e. information obtained through other activities and monitoring.
The sub-programme collects data on mass deaths of seabirds. Information can be obtained from different clubs and other sources of information, in particular public and amateur observations. The aim is to identify the number of mass deaths of seabirds and to identify the causes of death. This is, as a general rule, “passive” monitoring, i.e. information obtained through other activities and monitoring.
Features
Grazing birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Wading birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Wading birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Disturbance of species (e.g. where they breed, rest and feed) due to human presence
Surface-feeding birds
Disturbance of species (e.g. where they breed, rest and feed) due to human presence
Adverse effects on species or habitats
Benthic-feeding birds
Pelagic-feeding birds
Surface-feeding birds
Small toothed cetaceans
Seals
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Coastal ecosystems
Coastal ecosystems
Fish and shellfish harvesting (professional, recreational)
Pelagic-feeding birds
Surface-feeding birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Seals
Grazing birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Wading birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Wading birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Disturbance of species (e.g. where they breed, rest and feed) due to human presence
Surface-feeding birds
Disturbance of species (e.g. where they breed, rest and feed) due to human presence
Adverse effects on species or habitats
Benthic-feeding birds
Pelagic-feeding birds
Surface-feeding birds
Small toothed cetaceans
Seals
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Coastal ecosystems
Coastal ecosystems
Fish and shellfish harvesting (professional, recreational)
Pelagic-feeding birds
Surface-feeding birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Seals
Grazing birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Wading birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Wading birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Disturbance of species (e.g. where they breed, rest and feed) due to human presence
Surface-feeding birds
Disturbance of species (e.g. where they breed, rest and feed) due to human presence
Adverse effects on species or habitats
Benthic-feeding birds
Pelagic-feeding birds
Surface-feeding birds
Small toothed cetaceans
Seals
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Coastal ecosystems
Coastal ecosystems
Fish and shellfish harvesting (professional, recreational)
Pelagic-feeding birds
Surface-feeding birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Seals
Grazing birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Wading birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Wading birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Surface-feeding birds
Disturbance of species (e.g. where they breed, rest and feed) due to human presence
Surface-feeding birds
Disturbance of species (e.g. where they breed, rest and feed) due to human presence
Adverse effects on species or habitats
Benthic-feeding birds
Pelagic-feeding birds
Surface-feeding birds
Small toothed cetaceans
Seals
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Commercially exploited fish and shellfish
Coastal ecosystems
Coastal ecosystems
Fish and shellfish harvesting (professional, recreational)
Pelagic-feeding birds
Surface-feeding birds
Benthic-feeding birds
Grazing birds
Pelagic-feeding birds
Seals
Elements
  • Branta leucopsis
  • Aythya fuligula
  • Aythya marila
  • Melanitta fusca
  • Somateria mollissima
  • Anser anser
  • Branta leucopsis
  • Cygnus olor
  • Alca torda
  • Cepphus grylle
  • Mergus merganser
  • Mergus serrator
  • Phalacrocorax carbo
  • Podiceps cristatus
  • Uria aalge
  • Hydroprogne caspia
  • Larus argentatus
  • Larus canus
  • Larus marinus
  • Stercorarius parasiticus
  • Sterna hirundo
  • Sterna paradisaea
  • Sterna sandvicensis
  • Sternula albifrons
  • Arenaria interpres
  • Calidris alpina
  • Charadrius hiaticula
  • Haematopus ostralegus
  • Larus fuscus
  • Tadorna tadorna
  • Aythya fuligula
  • Aythya marila
  • Melanitta fusca
  • Somateria mollissima
  • Anser anser
  • Branta leucopsis
  • Cygnus olor
  • Alca torda
  • Cepphus grylle
  • Mergus merganser
  • Mergus serrator
  • Phalacrocorax carbo
  • Podiceps cristatus
  • Uria aalge
  • Hydroprogne caspia
  • Larus argentatus
  • Larus canus
  • Larus marinus
  • Stercorarius parasiticus
  • Sterna hirundo
  • Sterna paradisaea
  • Sterna sandvicensis
  • Sternula albifrons
  • Arenaria interpres
  • Calidris alpina
  • Charadrius hiaticula
  • Haematopus ostralegus
  • Larus fuscus
  • Tadorna tadorna
  • Aythya fuligula
  • Bucephala clangula
  • Clangula hyemalis
  • Melanitta fusca
  • Anas platyrhynchos
  • Cygnus olor
  • Cepphus grylle
  • Mergellus albellus
  • Mergus merganser
  • Mergus serrator
  • Phalacrocorax carbo
  • Larus argentatus
  • Larus canus
  • Larus marinus
  • Larus ridibundus
  • Aythya fuligula
  • Bucephala clangula
  • Clangula hyemalis
  • Melanitta fusca
  • Anas platyrhynchos
  • Cygnus olor
  • Cepphus grylle
  • Mergellus albellus
  • Mergus merganser
  • Mergus serrator
  • Phalacrocorax carbo
  • Larus argentatus
  • Larus canus
  • Larus marinus
  • Larus ridibundus
  • Not Applicable
  • Haliaeetus albicilla
  • Not Applicable
  • Haliaeetus albicilla
  • Benthic-feeding birds (grouped)
  • Pelagic-feeding birds (grouped)
  • Surface-feeding birds (grouped)
  • Phocoena phocoena
  • Halichoerus grypus
  • Pusa hispida
  • Esox spp.
  • Perca fluviatilis
  • Sander lucioperca
  • Esox spp.
  • Perca fluviatilis
  • Sander lucioperca
  • Esox spp.
  • Perca fluviatilis
  • Sander lucioperca
  • Fish community
  • Fish community
  • Not Applicable
  • Alca torda
  • Uria aalge
  • Sterna paradisaea
  • Aythya ferina
  • Aythya fuligula
  • Bucephala clangula
  • Clangula hyemalis
  • Somateria mollissima
  • Anas acuta
  • Anas clypeata
  • Anas crecca
  • Anas penelope
  • Anas platyrhynchos
  • Anser anser
  • Branta canadensis
  • Fulica atra
  • Mergus merganser
  • Mergus serrator
  • Halichoerus grypus
  • Pusa hispida
GES criteria
D1C1
D1C2
D1C2
D1C2
D1C2
D1C2
D1C4
D1C4
D1C4
D1C4
D1C4
D1C2
D1C2
D1C2
D1C2
D1C4
D1C4
D1C4
D1C4
D1C2
D1C3
D4C4
D8C2
D1C1
D1C1
D1C1
D1C1
D1C1
D3C1
D3C2
D3C3
D4C1
D4C2
NotRelevan
D1C3
D1C3
NotRelevan
NotRelevan
NotRelevan
NotRelevan
Parameters
  • Mortality (weight/volume; number of individuals)
  • Abundance (number of individuals)
  • Abundance (number of individuals)
  • Abundance (number of individuals)
  • Abundance (number of individuals)
  • Abundance (number of individuals)
  • Distribution (range)
  • Distribution (range)
  • Distribution (range)
  • Distribution (range)
  • Distribution (range)
  • Abundance (number of individuals)
  • Abundance (number of individuals)
  • Abundance (number of individuals)
  • Abundance (number of individuals)
  • Distribution (range)
  • Distribution (range)
  • Distribution (range)
  • Distribution (range)
  • Abundance (number of individuals)
  • Breeding success
  • Brood size
  • Survival rate
  • Productivity
  • Extent
  • Mortality (weight/volume; number of individuals)
  • Mortality (weight/volume; number of individuals)
  • Mortality (weight/volume; number of individuals)
  • Mortality (weight/volume; number of individuals)
  • Mortality (weight/volume; number of individuals)
  • Mortality (weight/volume; number of individuals)
  • Biomass of Spawning Stock (SSB)
  • Size distribution
  • Other
  • Abundance (number of individuals)
  • Other
  • Other
  • Other
  • Mortality (weight/volume; number of individuals)
  • Mortality (weight/volume; number of individuals)
  • Mortality (weight/volume; number of individuals)
  • Mortality (weight/volume; number of individuals)
Parameter Other
age
age
Abundance of Cyprinidae
Abundance of Cyprinidae
Fishing effort (days)
Mortality
Mortality
Spatial scope
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • Terrestrial part of MS
  • EEZ (or similar)
  • Terrestrial part of MS
  • Territorial waters
  • Territorial waters
  • Territorial waters
  • Territorial waters
Marine reporting units
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-AS
  • BAL-FI-AS-COAST
  • BAL-FI-AS-OFFSHORE
  • BAL-FI-BB
  • BAL-FI-BB-COAST
  • BAL-FI-BS
  • BAL-FI-BS-COAST
  • BAL-FI-BS-OFFSHORE
  • BAL-FI-GF
  • BAL-FI-GF-COAST
  • BAL-FI-GF-OFFSHORE
  • BAL-FI-NB
  • BAL-FI-NB-OFFSHORE
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-QK-OFFSHORE
  • BAL-FI-AS
  • BAL-FI-AS-COAST
  • BAL-FI-AS-OFFSHORE
  • BAL-FI-BB
  • BAL-FI-BB-COAST
  • BAL-FI-BS
  • BAL-FI-BS-COAST
  • BAL-FI-BS-OFFSHORE
  • BAL-FI-GF
  • BAL-FI-GF-COAST
  • BAL-FI-GF-OFFSHORE
  • BAL-FI-NB
  • BAL-FI-NB-OFFSHORE
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-QK-OFFSHORE
  • BAL-FI-AS
  • BAL-FI-AS-COAST
  • BAL-FI-AS-OFFSHORE
  • BAL-FI-BB
  • BAL-FI-BB-COAST
  • BAL-FI-BS
  • BAL-FI-BS-COAST
  • BAL-FI-BS-OFFSHORE
  • BAL-FI-GF
  • BAL-FI-GF-COAST
  • BAL-FI-GF-OFFSHORE
  • BAL-FI-NB
  • BAL-FI-NB-OFFSHORE
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-QK-OFFSHORE
  • BAL-FI-AS
  • BAL-FI-AS-COAST
  • BAL-FI-AS-OFFSHORE
  • BAL-FI-BB
  • BAL-FI-BB-COAST
  • BAL-FI-BS
  • BAL-FI-BS-COAST
  • BAL-FI-BS-OFFSHORE
  • BAL-FI-GF
  • BAL-FI-GF-COAST
  • BAL-FI-GF-OFFSHORE
  • BAL-FI-NB
  • BAL-FI-NB-OFFSHORE
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-QK-OFFSHORE
  • BAL-FI-AS
  • BAL-FI-AS-COAST
  • BAL-FI-AS-OFFSHORE
  • BAL-FI-BB
  • BAL-FI-BB-COAST
  • BAL-FI-BS
  • BAL-FI-BS-COAST
  • BAL-FI-BS-OFFSHORE
  • BAL-FI-GF
  • BAL-FI-GF-COAST
  • BAL-FI-GF-OFFSHORE
  • BAL-FI-NB
  • BAL-FI-NB-OFFSHORE
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-QK-OFFSHORE
  • BAL-FI-AS
  • BAL-FI-AS-COAST
  • BAL-FI-AS-OFFSHORE
  • BAL-FI-BB
  • BAL-FI-BB-COAST
  • BAL-FI-BS
  • BAL-FI-BS-COAST
  • BAL-FI-BS-OFFSHORE
  • BAL-FI-GF
  • BAL-FI-GF-COAST
  • BAL-FI-GF-OFFSHORE
  • BAL-FI-NB
  • BAL-FI-NB-OFFSHORE
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-QK-OFFSHORE
  • BAL-FI-AS
  • BAL-FI-AS-COAST
  • BAL-FI-AS-OFFSHORE
  • BAL-FI-BB
  • BAL-FI-BB-COAST
  • BAL-FI-BS
  • BAL-FI-BS-COAST
  • BAL-FI-BS-OFFSHORE
  • BAL-FI-GF
  • BAL-FI-GF-COAST
  • BAL-FI-GF-OFFSHORE
  • BAL-FI-NB
  • BAL-FI-NB-OFFSHORE
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-QK-OFFSHORE
  • BAL-FI-AS
  • BAL-FI-AS-COAST
  • BAL-FI-AS-OFFSHORE
  • BAL-FI-BB
  • BAL-FI-BB-COAST
  • BAL-FI-BS
  • BAL-FI-BS-COAST
  • BAL-FI-BS-OFFSHORE
  • BAL-FI-GF
  • BAL-FI-GF-COAST
  • BAL-FI-GF-OFFSHORE
  • BAL-FI-NB
  • BAL-FI-NB-OFFSHORE
  • BAL-FI-QK
  • BAL-FI-QK-COAST
  • BAL-FI-QK-OFFSHORE
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF-COAST
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF-COAST
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF-COAST
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF-COAST
  • BAL-FI-QK-COAST
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS
  • BAL-FI-BB
  • BAL-FI-BS
  • BAL-FI-GF
  • BAL-FI-NB
  • BAL-FI-QK
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF-COAST
  • BAL-FI-GF-OFFSHORE
  • BAL-FI-QK-COAST
  • BAL-FI-AS-COAST
  • BAL-FI-BB-COAST
  • BAL-FI-BS-COAST
  • BAL-FI-GF-COAST
  • BAL-FI-GF-OFFSHORE
  • BAL-FI-QK-COAST
  • BAL-FI
  • BAL-FI
  • BAL-FI
  • BAL-FI
Temporal scope (start date - end date)
1948-9999
1948-9999
1948-9999
1948-9999
1948-9999
1948-9999
1948-9999
1948-9999
1948-9999
1948-9999
1948-9999
1975-9999
1975-9999
1975-9999
1975-9999
1975-9999
1975-9999
1975-9999
1975-9999
1972-9999
1972-9999
1972-9999
1972-9999
1980-9999
1980-9999
1980-9999
1980-9999
1980-9999
1980-9999
1980-9999
1980-9999
1980-9999
1980-9999
1980-9999
1986-9999
1986-9999
1971-9999
1971-9999
1971-9999
1971-9999
Monitoring frequency
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Yearly
Continually
Continually
Continually
Continually
Continually
Continually
Continually
Continually
Continually
Continually
Continually
Other
Other
Continually
Continually
Continually
Continually
Monitoring type
  • Visual observation
  • Visual observation
  • Visual observation
  • Visual observation
  • Visual observation
  • Visual observation
  • Visual observation
  • Visual observation
  • Visual observation
  • Visual observation
  • Visual observation
  • Remote flight imagery
  • Visual observation
  • Remote flight imagery
  • Visual observation
  • Remote flight imagery
  • Visual observation
  • Remote flight imagery
  • Visual observation
  • Remote flight imagery
  • Visual observation
  • Remote flight imagery
  • Visual observation
  • Remote flight imagery
  • Visual observation
  • Remote flight imagery
  • Visual observation
  • In-situ sampling land/beach
  • In-situ sampling land/beach
  • In-situ sampling land/beach
  • In-situ sampling land/beach
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • In-situ sampling coastal
  • Visual observation
  • In-situ sampling coastal
  • Visual observation
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
  • Administrative data collection
Monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • Other monitoring method
  • HELCOM Guidelines for coordinated monitoring of wintering birds
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
Monitoring method other
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Marine breeding birds abundance and distribution - http://helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/birds/marine-breeding-birds-abundance-and-distribution/ Currently the whole counting network consists of 45 selected breeding areas situated in the archipelagos along the Finnish coast. About 20-30 of the areas are counted annually, but all areas are counted at least once every third year.
Koskimies & Väisänen 1991, Hario et al. 1993 & 1995, Lehikoinen et al. 2017
Koskimies & Väisänen 1991, Hario et al. 1993 & 1995, Lehikoinen et al. 2017
Koskimies & Väisänen 1991, Hario et al. 1993 & 1995, Lehikoinen et al. 2017
Koskimies & Väisänen 1991, Hario et al. 1993 & 1995, Lehikoinen et al. 2017
Koskimies & Väisänen 1991, Hario et al. 1993 & 1995, Lehikoinen et al. 2017
Koskimies & Väisänen 1991, Hario et al. 1993 & 1995, Lehikoinen et al. 2017
Koskimies & Väisänen 1991, Hario et al. 1993 & 1995, Lehikoinen et al. 2017
Koskimies & Väisänen 1991, Hario et al. 1993 & 1995, Lehikoinen et al. 2017
https://helcom.fi/wp-content/uploads/2019/12/Birds-Marine-bird-health.pdf
https://helcom.fi/wp-content/uploads/2019/12/Birds-Marine-bird-health.pdf
https://helcom.fi/wp-content/uploads/2019/12/Birds-Marine-bird-health.pdf
https://helcom.fi/wp-content/uploads/2019/12/Birds-Marine-bird-health.pdf
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery
Monitoring is based on sightings of general public and ornithologists
Monitoring is based on sightings of general public and ornithologists
Hunting organizations carry out game questionnaires. Hunting statistics are maintained by the hunting organizations and stored into a database. Data on species requiring special permit is obtained through the licensing system.
Hunting organizations carry out game questionnaires. Hunting statistics are maintained by the hunting organizations and stored into a database. Data on species requiring special permit is obtained through the licensing system.
Hunting organizations carry out game questionnaires. Hunting statistics are maintained by the hunting organizations and stored into a database. Data on species requiring special permit is obtained through the licensing system.
Hunting organizations carry out game questionnaires. Hunting statistics are maintained by the hunting organizations and stored into a database. Data on species requiring special permit is obtained through the licensing system.
Quality control
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
The calculation is based on cavity or other verification of the nesting, so that there are no ambiguous situations at the time of the calculation. For more information, see Hario and Rintala (2011).
Methods are according to Wetlands International- organizations standards. Methods described in HELCOM instructions (Helcom, 2015)
Methods are according to Wetlands International- organizations standards. Methods described in HELCOM instructions (Helcom, 2015)
Methods are according to Wetlands International- organizations standards. Methods described in HELCOM instructions (Helcom, 2015)
Methods are according to Wetlands International- organizations standards. Methods described in HELCOM instructions (Helcom, 2015)
Methods are according to Wetlands International- organizations standards. Methods described in HELCOM instructions (Helcom, 2015)
Methods are according to Wetlands International- organizations standards. Methods described in HELCOM instructions (Helcom, 2015)
Methods are according to Wetlands International- organizations standards. Methods described in HELCOM instructions (Helcom, 2015)
Methods are according to Wetlands International- organizations standards. Methods described in HELCOM instructions (Helcom, 2015)
Method developed in co-operation with Swedish and German authorities under HELCOM
Method developed in co-operation with Swedish and German authorities under HELCOM
Method developed in co-operation with Swedish and German authorities under HELCOM
Method developed in co-operation with Swedish and German authorities under HELCOM
Quality control — https://stat.luke.fi/en/commercial-marine-fishery
Quality control - https://stat.luke.fi/en/commercial-marine-fishery
Quality control - https://stat.luke.fi/en/commercial-marine-fishery
Quality control - https://stat.luke.fi/en/commercial-marine-fishery
Quality control - https://stat.luke.fi/en/commercial-marine-fishery
Quality control - https://stat.luke.fi/en/commercial-marine-fishery
Quality control - https://stat.luke.fi/en/commercial-marine-fishery
Quality control - https://stat.luke.fi/en/commercial-marine-fishery
Quality control - https://stat.luke.fi/en/commercial-marine-fishery
Quality control — https://stat.luke.fi/en/commercial-marine-fishery
Quality control - https://stat.luke.fi/en/commercial-marine-fishery
No specified quality control. Data comes from various sources, so mass mortalities are most likely reported
No specified quality control. Data comes from various sources, so mass mortalities are most likely reported
https://stat.luke.fi/tilasto/4428/laatuseloste/4697
https://stat.luke.fi/tilasto/4428/laatuseloste/4697
https://stat.luke.fi/tilasto/4428/laatuseloste/4697
https://stat.luke.fi/tilasto/4428/laatuseloste/4697
Data management
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Primary data only for researchers. Results at HELCOM Biodiversity database Summary of result at HELCOM indicators
Data stored in Finnish Museum of Natural History database. Data reported yearly to Wetlands Internationals database. HELCOM publishes indicator results yearly and publsihed indicator data.
Data stored in Finnish Museum of Natural History database. Data reported yearly to Wetlands Internationals database. HELCOM publishes indicator results yearly and publsihed indicator data.
Data stored in Finnish Museum of Natural History database. Data reported yearly to Wetlands Internationals database. HELCOM publishes indicator results yearly and publsihed indicator data.
Data stored in Finnish Museum of Natural History database. Data reported yearly to Wetlands Internationals database. HELCOM publishes indicator results yearly and publsihed indicator data.
Data stored in Finnish Museum of Natural History database. Data reported yearly to Wetlands Internationals database. HELCOM publishes indicator results yearly and publsihed indicator data.
Data stored in Finnish Museum of Natural History database. Data reported yearly to Wetlands Internationals database. HELCOM publishes indicator results yearly and publsihed indicator data.
Data stored in Finnish Museum of Natural History database. Data reported yearly to Wetlands Internationals database. HELCOM publishes indicator results yearly and publsihed indicator data.
Data stored in Finnish Museum of Natural History database. Data reported yearly to Wetlands Internationals database. HELCOM publishes indicator results yearly and publsihed indicator data.
Primary data stored in Finnish Museum of Natural History. HELCOM publishes indicator data.
Primary data stored in Finnish Museum of Natural History. HELCOM publishes indicator data.
Primary data stored in Finnish Museum of Natural History. HELCOM publishes indicator data.
Primary data stored in Finnish Museum of Natural History. HELCOM publishes indicator data.
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
National database:http://www.ely-keskus.fi/web/ely/saalisseuranta. Summary statisitcs:https://statdb.luke.fi/PXWeb/pxweb/fi/LUKE/LUKE__06 Kala ja riista__02 Rakenne ja tuotanto__02 Kaupallinen kalastus merella/?tablelist
Mortality data not publicly available Bird ringing data available online
Mortality data not publicly available Bird ringing data available online
Primary data only accessible for researchers
Primary data only accessible for researchers
Primary data only accessible for researchers
Primary data only accessible for researchers
Data access
Related indicator/name
Contact
References
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M. & Rintala J. 2011. Saaristolintukantojen kehitys Suomessa 1986 –2010. – Linnut vuosikirja 2010: 40 – 51
Hario, M., Lammi, E., Mikkola, M. & Södersved, J. 1993: Ovatko Ahvenanmaan vesilinnut "talvenkärkkyjiä" – kansainvälisten vesilintulaskentojen tuloksia vuosilta 1968-92. – Suomen Riista 39: 21– 32. Hario, M., Lammi, E., Mikkola, M., Södersved, J. 1995: January counts of waterfowl in SW Finland: the dependence on ice situation. – Ring 15 (1–2): 216 –222. HELCOM (2015), HELCOM guidelines for coordinated monitoring of wintering birds. 13 s. Koskimies & Väisänen (1991): Monitoring Bird Populations – A Manual of Methods Applied in Finland. – Zoological Museum, Finnish Museum of Natural History, University of Helsinki. Lehikoinen, A., Kuntze, K., Lehtiniemi, T. Mikkola-Roos, M. & Toivanen, T. 2017: Suomen keskitalven vesilintukantojen kannanarviot vuonna 2016 - muuttuva Suomi osana kansainvälistä seurantaa. - Linnut vuosikirja 2016:6-15.
Hario, M., Lammi, E., Mikkola, M. & Södersved, J. 1993: Ovatko Ahvenanmaan vesilinnut "talvenkärkkyjiä" – kansainvälisten vesilintulaskentojen tuloksia vuosilta 1968-92. – Suomen Riista 39: 21– 32. Hario, M., Lammi, E., Mikkola, M., Södersved, J. 1995: January counts of waterfowl in SW Finland: the dependence on ice situation. – Ring 15 (1–2): 216 –222. HELCOM (2015), HELCOM guidelines for coordinated monitoring of wintering birds. 13 s. Koskimies & Väisänen (1991): Monitoring Bird Populations – A Manual of Methods Applied in Finland. – Zoological Museum, Finnish Museum of Natural History, University of Helsinki. Lehikoinen, A., Kuntze, K., Lehtiniemi, T. Mikkola-Roos, M. & Toivanen, T. 2017: Suomen keskitalven vesilintukantojen kannanarviot vuonna 2016 - muuttuva Suomi osana kansainvälistä seurantaa. - Linnut vuosikirja 2016:6-15.
Hario, M., Lammi, E., Mikkola, M. & Södersved, J. 1993: Ovatko Ahvenanmaan vesilinnut "talvenkärkkyjiä" – kansainvälisten vesilintulaskentojen tuloksia vuosilta 1968-92. – Suomen Riista 39: 21– 32. Hario, M., Lammi, E., Mikkola, M., Södersved, J. 1995: January counts of waterfowl in SW Finland: the dependence on ice situation. – Ring 15 (1–2): 216 –222. HELCOM (2015), HELCOM guidelines for coordinated monitoring of wintering birds. 13 s. Koskimies & Väisänen (1991): Monitoring Bird Populations – A Manual of Methods Applied in Finland. – Zoological Museum, Finnish Museum of Natural History, University of Helsinki. Lehikoinen, A., Kuntze, K., Lehtiniemi, T. Mikkola-Roos, M. & Toivanen, T. 2017: Suomen keskitalven vesilintukantojen kannanarviot vuonna 2016 - muuttuva Suomi osana kansainvälistä seurantaa. - Linnut vuosikirja 2016:6-15.
Hario, M., Lammi, E., Mikkola, M. & Södersved, J. 1993: Ovatko Ahvenanmaan vesilinnut "talvenkärkkyjiä" – kansainvälisten vesilintulaskentojen tuloksia vuosilta 1968-92. – Suomen Riista 39: 21– 32. Hario, M., Lammi, E., Mikkola, M., Södersved, J. 1995: January counts of waterfowl in SW Finland: the dependence on ice situation. – Ring 15 (1–2): 216 –222. HELCOM (2015), HELCOM guidelines for coordinated monitoring of wintering birds. 13 s. Koskimies & Väisänen (1991): Monitoring Bird Populations – A Manual of Methods Applied in Finland. – Zoological Museum, Finnish Museum of Natural History, University of Helsinki. Lehikoinen, A., Kuntze, K., Lehtiniemi, T. Mikkola-Roos, M. & Toivanen, T. 2017: Suomen keskitalven vesilintukantojen kannanarviot vuonna 2016 - muuttuva Suomi osana kansainvälistä seurantaa. - Linnut vuosikirja 2016:6-15.
Hario, M., Lammi, E., Mikkola, M. & Södersved, J. 1993: Ovatko Ahvenanmaan vesilinnut "talvenkärkkyjiä" – kansainvälisten vesilintulaskentojen tuloksia vuosilta 1968-92. – Suomen Riista 39: 21– 32. Hario, M., Lammi, E., Mikkola, M., Södersved, J. 1995: January counts of waterfowl in SW Finland: the dependence on ice situation. – Ring 15 (1–2): 216 –222. HELCOM (2015), HELCOM guidelines for coordinated monitoring of wintering birds. 13 s. Koskimies & Väisänen (1991): Monitoring Bird Populations – A Manual of Methods Applied in Finland. – Zoological Museum, Finnish Museum of Natural History, University of Helsinki. Lehikoinen, A., Kuntze, K., Lehtiniemi, T. Mikkola-Roos, M. & Toivanen, T. 2017: Suomen keskitalven vesilintukantojen kannanarviot vuonna 2016 - muuttuva Suomi osana kansainvälistä seurantaa. - Linnut vuosikirja 2016:6-15.
Hario, M., Lammi, E., Mikkola, M. & Södersved, J. 1993: Ovatko Ahvenanmaan vesilinnut "talvenkärkkyjiä" – kansainvälisten vesilintulaskentojen tuloksia vuosilta 1968-92. – Suomen Riista 39: 21– 32. Hario, M., Lammi, E., Mikkola, M., Södersved, J. 1995: January counts of waterfowl in SW Finland: the dependence on ice situation. – Ring 15 (1–2): 216 –222. HELCOM (2015), HELCOM guidelines for coordinated monitoring of wintering birds. 13 s. Koskimies & Väisänen (1991): Monitoring Bird Populations – A Manual of Methods Applied in Finland. – Zoological Museum, Finnish Museum of Natural History, University of Helsinki. Lehikoinen, A., Kuntze, K., Lehtiniemi, T. Mikkola-Roos, M. & Toivanen, T. 2017: Suomen keskitalven vesilintukantojen kannanarviot vuonna 2016 - muuttuva Suomi osana kansainvälistä seurantaa. - Linnut vuosikirja 2016:6-15.
Hario, M., Lammi, E., Mikkola, M. & Södersved, J. 1993: Ovatko Ahvenanmaan vesilinnut "talvenkärkkyjiä" – kansainvälisten vesilintulaskentojen tuloksia vuosilta 1968-92. – Suomen Riista 39: 21– 32. Hario, M., Lammi, E., Mikkola, M., Södersved, J. 1995: January counts of waterfowl in SW Finland: the dependence on ice situation. – Ring 15 (1–2): 216 –222. HELCOM (2015), HELCOM guidelines for coordinated monitoring of wintering birds. 13 s. Koskimies & Väisänen (1991): Monitoring Bird Populations – A Manual of Methods Applied in Finland. – Zoological Museum, Finnish Museum of Natural History, University of Helsinki. Lehikoinen, A., Kuntze, K., Lehtiniemi, T. Mikkola-Roos, M. & Toivanen, T. 2017: Suomen keskitalven vesilintukantojen kannanarviot vuonna 2016 - muuttuva Suomi osana kansainvälistä seurantaa. - Linnut vuosikirja 2016:6-15.
Hario, M., Lammi, E., Mikkola, M. & Södersved, J. 1993: Ovatko Ahvenanmaan vesilinnut "talvenkärkkyjiä" – kansainvälisten vesilintulaskentojen tuloksia vuosilta 1968-92. – Suomen Riista 39: 21– 32. Hario, M., Lammi, E., Mikkola, M., Södersved, J. 1995: January counts of waterfowl in SW Finland: the dependence on ice situation. – Ring 15 (1–2): 216 –222. HELCOM (2015), HELCOM guidelines for coordinated monitoring of wintering birds. 13 s. Koskimies & Väisänen (1991): Monitoring Bird Populations – A Manual of Methods Applied in Finland. – Zoological Museum, Finnish Museum of Natural History, University of Helsinki. Lehikoinen, A., Kuntze, K., Lehtiniemi, T. Mikkola-Roos, M. & Toivanen, T. 2017: Suomen keskitalven vesilintukantojen kannanarviot vuonna 2016 - muuttuva Suomi osana kansainvälistä seurantaa. - Linnut vuosikirja 2016:6-15.
Stjernberg, T., Koivusaari, J., Högmander, J., Nuuja, I. & Lokki, H. 2011: Suomen merikotkat 2009 –2010. – Linnut-vuosikirja 2010: 18 –27. https://helcom.fi/media/core%20indicators/White-tailed-sea-eagle-productivity-HELCOM-core-indicator-2018.pdf
Stjernberg, T., Koivusaari, J., Högmander, J., Nuuja, I. & Lokki, H. 2011: Suomen merikotkat 2009 –2010. – Linnut-vuosikirja 2010: 18 –27. https://helcom.fi/media/core%20indicators/White-tailed-sea-eagle-productivity-HELCOM-core-indicator-2018.pdf
Stjernberg, T., Koivusaari, J., Högmander, J., Nuuja, I. & Lokki, H. 2011: Suomen merikotkat 2009 –2010. – Linnut-vuosikirja 2010: 18 –27. https://helcom.fi/media/core%20indicators/White-tailed-sea-eagle-productivity-HELCOM-core-indicator-2018.pdf
Stjernberg, T., Koivusaari, J., Högmander, J., Nuuja, I. & Lokki, H. 2011: Suomen merikotkat 2009 –2010. – Linnut-vuosikirja 2010: 18 –27. https://helcom.fi/media/core%20indicators/White-tailed-sea-eagle-productivity-HELCOM-core-indicator-2018.pdf
Hario, M., Hokkanen, T., Malkio, H. 1993. Itäisen Suomenlahden lintukuolemat. – Suomen Riista 39:7–20 Suleva, E. & Rintala, J. 2013. Ruokkilinnut Itämeren tilan indikaattoreina. Helsinki: RKTL:n työraportteja 1/2013. Riista- ja kalatalouden tutkimuslaitos. ISBN: 978-951-776-945-7. Mikkola-Roos, M. , Below, A., Lehikoinen, A & Rintala, J. 2018: Meriympäristön tila 2011-2016 : Merilinnut. Julk.: Korpinen, S., Laamanen, M., Suomela, J., Paavilainen, P., Lahtinen, T. & Ekebom, J. 2018. (toim.) Suomen meriympäristön tila 2018. Helsinki, Suomen ympäristökeskus. Ss. 198-207. SYKE:n julkaisuja 2018, 4. ISBN 978-952-11-4967-2 (nid.), 978-952-11-4968-9 (PDF), ISSN 2323-8895, (painettu), 2323-8909 (verkkojulkaisu). 2018: http://hdl.handle.net/10138/274086
Hario, M., Hokkanen, T., Malkio, H. 1993. Itäisen Suomenlahden lintukuolemat. – Suomen Riista 39:7–20 Suleva, E. & Rintala, J. 2013. Ruokkilinnut Itämeren tilan indikaattoreina. Helsinki: RKTL:n työraportteja 1/2013. Riista- ja kalatalouden tutkimuslaitos. ISBN: 978-951-776-945-7. Mikkola-Roos, M. , Below, A., Lehikoinen, A & Rintala, J. 2018: Meriympäristön tila 2011-2016 : Merilinnut. Julk.: Korpinen, S., Laamanen, M., Suomela, J., Paavilainen, P., Lahtinen, T. & Ekebom, J. 2018. (toim.) Suomen meriympäristön tila 2018. Helsinki, Suomen ympäristökeskus. Ss. 198-207. SYKE:n julkaisuja 2018, 4. ISBN 978-952-11-4967-2 (nid.), 978-952-11-4968-9 (PDF), ISSN 2323-8895, (painettu), 2323-8909 (verkkojulkaisu). 2018: http://hdl.handle.net/10138/274086