Member State report / Art11 / 2014-2020 / D4 / 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 | D4 Food webs/D1 Ecosystems |
| Member State | Finland |
| Region/subregion | Baltic Sea |
| Reported by | Reporter not found |
| Report date | -; 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_D1_4_6_WaterColumnHabitats |
MP_D1_4_6_WaterColumnHabitats |
MP_D1_4_6_WaterColumnHabitats |
MP_D1_4_6_WaterColumnHabitats |
MP_D1_4_6_WaterColumnHabitats |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| 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 |
BALFI-D01,04,06pel |
BALFI-D01,04,06pel |
BALFI-D01,04,06pel |
BALFI-D01,04,06pel |
BALFI-D01,04,06pel |
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| Monitoring programme | Marine Unit ID |
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| 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-D01,04,06pel |
BALFI-D01,04,06pel |
BALFI-D01,04,06pel |
BALFI-D01,04,06pel |
BALFI-D01,04,06pel |
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| 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 is available in the HELCOM Monitoring manual (Biodiversity - Water column habitats) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#WaterColumnHabitats
General information on Sub-programmes is available in the HELCOM Monitoring manual (Hydrography) at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/ |
General information is available in the HELCOM Monitoring manual (Biodiversity - Water column habitats) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#WaterColumnHabitats
General information on Sub-programmes is available in the HELCOM Monitoring manual (Hydrography) at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/ |
General information is available in the HELCOM Monitoring manual (Biodiversity - Water column habitats) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#WaterColumnHabitats
General information on Sub-programmes is available in the HELCOM Monitoring manual (Hydrography) at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/ |
General information is available in the HELCOM Monitoring manual (Biodiversity - Water column habitats) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#WaterColumnHabitats
General information on Sub-programmes is available in the HELCOM Monitoring manual (Hydrography) at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/ |
General information is available in the HELCOM Monitoring manual (Biodiversity - Water column habitats) - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/introduction#WaterColumnHabitats
General information on Sub-programmes is available in the HELCOM Monitoring manual (Hydrography) at: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/ |
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| Q5e - Natural variability |
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| 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 |
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 |
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 |
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 |
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. |
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. |
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| Q5g - Gap-filling date for GES assessment | By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
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| Q5h - Plans to implement monitoring for GES assessment |
No immediate development needs.
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No immediate development needs.
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No immediate development needs.
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No immediate development needs.
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No immediate development needs.
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No immediate development needs.
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No immediate development needs.
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No immediate development needs.
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No immediate development needs.
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No immediate development needs.
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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.
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No immediate development needs.
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No immediate development needs.
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No immediate development needs.
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No immediate development needs.
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| 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 09 Target 19 Target 23 |
Target 09 Target 19 Target 23 |
Target 09 Target 19 Target 23 |
Target 09 Target 19 Target 23 |
Target 09 Target 19 Target 23 |
| 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 09 Target 19 Target 23 |
Target 09 Target 19 Target 23 |
Target 09 Target 19 Target 23 |
Target 09 Target 19 Target 23 |
Target 09 Target 19 Target 23 |
| Q6b - Adequacy for assessment of targets | Q6b_SuitableData | Y |
Y |
Y |
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 |
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 |
Y |
Y |
Y |
| Q6c - Target updating | Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
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| 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 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) |
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| Q6e - Gap-filling date for targets assessment | By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
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| Q6f - Plans to implement monitoring for targets assessment |
Program is fully adequate
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Program is fully adequate
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| Q7a - Relevant activities |
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| 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
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No monitoring of activities
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No monitoring of activities
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No monitoring activities
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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. |
The number and location of bathing sites are monitored under this program. Their effects on water quality assessed under the Bathing Water Directive. |
The number and location of bathing sites are monitored under this program. Their effects on water quality assessed under the Bathing Water Directive. |
The number and location of bathing sites are monitored under this program. Their effects on water quality assessed under the Bathing Water Directive. |
The number and location of bathing sites are monitored under this program. Their effects on water quality assessed under the Bathing Water Directive. |
The number and location of bathing sites are monitored under this program. Their effects on water quality assessed under the Bathing Water Directive. |
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| 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 |
By2014 |
By2014 |
By2014 |
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| Q8a - Links to existing Monitoring Programmes |
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| 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-D01,04,06pel-1 |
BALFI-D01,04,06pel-2 |
BALFI-D01,04,06pel-3 |
BALFI-D01,04,06pel-4 |
BALFI-D01,04,06pel-5 |
| 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 |
Mobile species - abundance and/or biomass |
Plankton blooms (biomass, frequency) |
Microbial pathogen levels - in water column (bathing waters) |
Water column - hydrological characteristics |
Water column - physical characteristics |
| 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-D01,04,06pel-1 |
BALFI-D01,04,06pel-2 |
BALFI-D01,04,06pel-3 |
BALFI-D01,04,06pel-4 |
BALFI-D01,04,06pel-5 |
| 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 |
Mobile species - abundance and/or biomass |
Plankton blooms (biomass, frequency) |
Microbial pathogen levels - in water column (bathing waters) |
Water column - hydrological characteristics |
Water column - physical characteristics |
| Q4k - Monitoring purpose | StateImpact |
StateImpact |
StateImpact |
StateImpact |
StateImpact |
StateImpact |
StateImpact |
StateImpact |
StateImpact |
StateImpact |
StateImpact |
StateImpact |
StateImpact |
StateImpact Pressurse Activities |
StateImpact |
StateImpact |
StateImpact Activities |
StateImpact |
StateImpact |
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| 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: Zooplankton species composition, abundance and biomass - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/zooplankton/zooplankton-species-composition-abundance-and-biomass |
This sub-programme also refers to the monitoring which has been reported under the Water Framework Directive. Further information on the sub-programme is described in:
HELCOM Monitoring manual - Sub-programme: Phytoplankton species composition, abundance and biomass - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/phytoplankton/species-composition-abundance-and-biomass |
This sub-programme refers to the monitoring which has been reported under the Bathing water directive (2006/7/EU) and the Water Framework Directive.
Essential information describing this national sub-programme is available at:
EEA State of bathing water site: http://www.eea.europa.eu/themes/water/interactive/bathing/state-of-bathing-waters-1 |
This sub-programme also refers to the monitoring which has been reported under the Water Framework Directive.
Further information describing this sub-programme is available in:
HELCOM Monitoring manual - Sub-programme: Water column hydrological characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/temperature-salinity-transparency-turbidity |
Essential information describing this sub-programme is available in:
HELCOM Monitoring manual - Sub-programme: Water column physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/waves-currents-%28sealevel%29
HELCOM Monitoring manual - Sub-programme: Ice - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/ice |
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| Q5c - Features | Q5c - Habitats |
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| Q5c - Features | Q5c - Species list |
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| Q5c - Features | Q5c - Physical/Chemical features |
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| Q5c - Features | Q5c - Pressures |
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| Q9a - Elements |
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| Q5a - GES criteria | Relevant GES criteria |
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| Q5b - GES indicators | Relevant GES indicators |
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| Q9b - Parameters monitored (state/impact) | Species distribution |
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| Q9b - Parameters monitored (state/impact) | Species population size |
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| Q9b - Parameters monitored (state/impact) | Species population characteristics |
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| Q9b - Parameters monitored (state/impact) | Species impacts |
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| Q9b - Parameters monitored (state/impact) | Habitat distribution |
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| Q9b - Parameters monitored (state/impact) | Habitat extent |
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| Q9b - Parameters monitored (state/impact) | Habitat condition (physical-chemical) |
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| Q9b - Parameters monitored (state/impact) | Habitat condition (biological) |
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| Q9b - Parameters monitored (state/impact) | Habitat impacts | |||||||||||||||||||
| Q9b - Parameters monitored (pressures) | Pressure input |
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| Q9b - Parameters monitored (pressures) | Pressure output |
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| Q9b - Parameters monitored (activity) | Activity |
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| 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 |
TerritorialWaters EEZ BeyondMSwaters |
TerritorialWaters EEZ BeyondMSwaters |
WFD_CW |
WFD_CW TerritorialWaters EEZ BeyondMSwaters |
WFD_CW TerritorialWaters EEZ BeyondMSwaters |
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| 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: Zooplankton species composition, abundance and biomass - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/zooplankton/zooplankton-species-composition-abundance-and-biomass |
HELCOM Monitoring manual - Sub-programme: Phytoplankton species composition, abundance and biomass - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/phytoplankton/species-composition-abundance-and-biomass |
Monitoring is done only on public bathing sites along the Finnish coast. One of the main sources of pathogens are the public bathing sites. |
HELCOM Monitoring manual - Sub-programme: Water column hydrological characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/temperature-salinity-transparency-turbidity |
HELCOM Monitoring manual - Sub-programme: Water column physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/waves-currents-%28sealevel%29
HELCOM Monitoring manual - Sub-programme: Ice - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/ice |
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| Marine Unit IDs |
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| 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 |
1976-9999 |
1979-9999 |
2009-9999 |
1979-9999 |
1791-9999 |
| Q9h - Temporal resolution of sampling |
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| 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: Zooplankton species composition, abundance and biomass - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/zooplankton/zooplankton-species-composition-abundance-and-biomass |
HELCOM Monitoring manual - Sub-programme: Phytoplankton species composition, abundance and biomass - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/phytoplankton/species-composition-abundance-and-biomass |
National Supervisory Authority for Welfare and Health - http://www.valvira.fi/files/ohjeet/Yleisten_uimarantojen_uimaveden_valvonta.pdf (in Finnish) |
HELCOM Monitoring manual - Sub-programme: Water column hydrological characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/temperature-salinity-transparency-turbidity |
HELCOM Monitoring manual - Sub-programme: Water column physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/waves-currents-%28sealevel%29
HELCOM Monitoring manual - Sub-programme: Ice - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/ice |
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| 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). |
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| Q9e - Quality assurance |
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| Q9f - Quality control | RealandDelayedValidation |
RealandDelayedValidation |
Unknown |
RealandDelayedValidation |
RealandDelayedValidation |
Unknown |
Unknown |
RealValidation |
RealandDelayedValidation |
Unknown |
RealandDelayedValidation |
RealandDelayedValidation |
RealandDelayedValidation |
Unknown |
RealandDelayedValidation |
RealandDelayedValidation |
Unknown |
RealandDelayedValidation |
RealandDelayedValidation |
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| Q9g - Spatial resolution of sampling | Q9g - Proportion of area covered % | 100 |
100 |
15 |
100 |
100 |
100 |
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| 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: Zooplankton species composition, abundance and biomass - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/zooplankton/zooplankton-species-composition-abundance-and-biomass |
HELCOM Monitoring manual - Sub-programme: Phytoplankton species composition, abundance and biomass - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/phytoplankton/species-composition-abundance-and-biomass |
80 coastal sampling sites are sampled 4 times per year |
HELCOM Monitoring manual - Sub-programme: Water column hydrological characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/temperature-salinity-transparency-turbidity |
HELCOM Monitoring manual - Sub-programme: Water column physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/waves-currents-%28sealevel%29
HELCOM Monitoring manual - Sub-programme: Ice - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/ice |
| 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 |
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| Q10a - Scale for aggregation of data |
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| 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 |
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| 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 |
UnprocessedData ProcessedData DataProducts |
UnprocessedData ProcessedData DataProducts |
ProcessedData DataProducts |
UnprocessedData ProcessedData DataProducts |
UnprocessedData 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 |
URLview |
LocationInternationalDC |
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 |
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 |
HabitatsBiotopes SeaRegions SpeciesDistribution |
HabitatsBiotopes SeaRegions SpeciesDistribution |
ManagementZonesReportingUnits |
Hydrography |
Hydrography |
| 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 |
2015-12 |
2015-12 |
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| Q10c - Access to monitoring data | Q10c - Data update frequency | Yearly |
Yearly |
Asneeded |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
6yearly |
Unknown |
Yearly |
Unknown |
Yearly |
Unknown |
| 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
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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: Zooplankton mean size and total abundance - http://www.helcom.fi/Core%20Indicators/HELCOM-CoreIndicator-Zooplankton_mean_size_and_total_abundance.pdf
Raw data available on NOAA/COPEPOD-plankton database - http://www.st.nmfs.noaa.gov/plankton/content/region_baltic.html
More information on data access is available in the HELCOM Monitoring manual - Sub-programme: Zooplankton species composition, abundance and biomass - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/zooplankton/zooplankton-species-composition-abundance-and-biomass |
ICES data portal - http://www.ices.dk/marine-data/data-portals/Pages/DOME.aspx
HELCOM Data and Map services - http://helcom.fi/baltic-sea-trends/data-maps
Soon also available on Finnish open data portal OIVA - https://wwwp2.ymparisto.fi/scripts/oiva.asp (in Finnish)
More information on data access is available in the HELCOM Monitoring manual - Sub-programme: Phytoplankton species composition, abundance and biomass - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/phytoplankton/species-composition-abundance-and-biomass |
Information can be found at EEA State of bathing water site - http://www.eea.europa.eu/themes/water/interactive/bathing/state-of-bathing-waters-1
and at the National Supervisory Authority for Welfare and Health - http://www.valvira.fi/files/ohjeet/Yleisten_uimarantojen_uimaveden_valvonta.pdf (in Finnish) |
The data is open access and available to the EEA though HELCOM and ICES Web access points.
Finnish Meteorological Institute Open Data Manual - http://en.ilmatieteenlaitos.fi/open-data-manual
SYKE public data portal OIVA in Finnish - https://wwwp2.ymparisto.fi/scripts/oiva.asp
Information on data access is also available in the HELCOM Monitoring manual - Sub-programme: Water column hydrological characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/temperature-salinity-transparency-turbidity |
Finnish Meteorological Institute Open Data Manual - http://en.ilmatieteenlaitos.fi/open-data-manual
More information on data access is available in the HELCOM Monitoring manual:
- Sub-programme: Water column physical characteristics - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/waves-currents-%28sealevel%29
- Sub-programme: Ice - http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/hydrography/ice |
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D4/D1 |
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D4/D1 |
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D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
D4/D1 |
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D4/D1 |
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Monitoring strategy description |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
Food webs are monitored by the monitoring programmes producing information of marine mammals (apex predators), seabirds (apex predators, fish feeders, benthic feeders, grazers), fish (predatory, planktivorous, benthic feeders), benthic invertebrates (deposit feeders, filter feeders), zooplankton and primary producers (phytoplankton, macrophytes). |
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 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in 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 |
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Related targets |
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Coverage of targets |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Related measures |
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Coverage of measures |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Related monitoring programmes |
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Programme code |
BALFI-D01,04,06ben-1 |
BALFI-D01,04,06ben-1 |
BALFI-D01,04,06ben-1 |
BALFI-D01,04,06ben-1 |
BALFI-D01,04,06ben-1 |
BALFI-D01,04,06ben-1 |
BALFI-D01,04,06ben-1 |
BALFI-D01,04,06ben-1 |
BALFI-D01,04,06ben-1 |
BALFI-D01,04,06ben-1 |
BALFI-D01,04,06ben-2 |
BALFI-D01,04,06ben-2 |
BALFI-D01,04,06ben-2 |
BALFI-D01,04,06ben-2 |
BALFI-D01,04,06ben-2 |
BALFI-D01,04,06ben-2 |
BALFI-D01,04,06ben-2 |
BALFI-D01,04,06ben-2 |
BALFI-D01,04,06ben-2 |
BALFI-D01,04,06ben-2 |
BALFI-D01,04,06ben-2 |
BALFI-D01,04,06ben-2 |
BALFI-D01,04,06ben-2 |
BALFI-D01,04,06ben-3 |
BALFI-D01,04,06ben-3 |
BALFI-D01,04,06ben-3 |
BALFI-D01,04,06ben-3 |
BALFI-D01,04,06ben-3 |
BALFI-D01,04,06ben-3 |
BALFI-D01,04,06ben-5 |
BALFI-D01,04,06ben-5 |
BALFI-D01,04,06ben-5 |
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-D01,04,06mam-1 |
BALFI-D01,04,06mam-1 |
BALFI-D01,04,06mam-2 |
BALFI-D01,04,06mam-2 |
BALFI-D01,04,06mam-3 |
BALFI-D01,04,06mam-3 |
BALFI-D01,04,06pel-1 |
BALFI-D01,04,06pel-1 |
BALFI-D01,04,06pel-1 |
BALFI-D01,04,06pel-1 |
BALFI-D01,04,06pel-1 |
BALFI-D01,04,06pel-1 |
BALFI-D01,04,06pel-2 |
BALFI-D01,04,06pel-2 |
BALFI-D01,04,06pel-2 |
BALFI-D01,04,06pel-2 |
BALFI-D01,04,06pel-2 |
BALFI-D01,04,06pel-2 |
BALFI-D03-1 |
BALFI-D03-1 |
BALFI-D03-1 |
BALFI-D03-1 |
BALFI-D03-1 |
BALFI-D03-1 |
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-D05-3 |
BALFI-D05-3 |
BALFI-D05-3 |
BALFI-D05-3 |
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 |
Offshore soft bottom macrozoobenthos |
Offshore soft bottom macrozoobenthos |
Offshore soft bottom macrozoobenthos |
Offshore soft bottom macrozoobenthos |
Offshore soft bottom macrozoobenthos |
Offshore soft bottom macrozoobenthos |
Offshore soft bottom macrozoobenthos |
Offshore soft bottom macrozoobenthos |
Offshore soft bottom macrozoobenthos |
Offshore soft bottom macrozoobenthos |
Coastal waters soft bottom fauna |
Coastal waters soft bottom fauna |
Coastal waters soft bottom fauna |
Coastal waters soft bottom fauna |
Coastal waters soft bottom fauna |
Coastal waters soft bottom fauna |
Coastal waters soft bottom fauna |
Coastal waters soft bottom fauna |
Coastal waters soft bottom fauna |
Coastal waters soft bottom fauna |
Coastal waters soft bottom fauna |
Coastal waters soft bottom fauna |
Coastal waters soft bottom fauna |
Coastal hard bottom macroalgae and blue mussel communities |
Coastal hard bottom macroalgae and blue mussel communities |
Coastal hard bottom macroalgae and blue mussel communities |
Coastal hard bottom macroalgae and blue mussel communities |
Coastal hard bottom macroalgae and blue mussel communities |
Coastal hard bottom macroalgae and blue mussel communities |
Soft bottom macrophytes |
Soft bottom macrophytes |
Soft bottom macrophytes |
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 |
Seal adundance |
Seal adundance |
Seal state of health |
Seal state of health |
Abundance and distribution of harbour porpoises |
Abundance and distribution of harbour porpoises |
Zooplankton species composition and abundance |
Zooplankton species composition and abundance |
Zooplankton species composition and abundance |
Zooplankton species composition and abundance |
Zooplankton species composition and abundance |
Zooplankton species composition and abundance |
Phytoplankton species composition, abundance and biomass |
Phytoplankton species composition, abundance and biomass |
Phytoplankton species composition, abundance and biomass |
Phytoplankton species composition, abundance and biomass |
Phytoplankton species composition, abundance and biomass |
Phytoplankton species composition, abundance and biomass |
Fisheries data collection |
Fisheries data collection |
Fisheries data collection |
Fisheries data collection |
Fisheries data collection |
Fisheries data collection |
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 |
Phytoplankton pigments |
Phytoplankton pigments |
Phytoplankton pigments |
Phytoplankton pigments |
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 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
New programme |
New programme |
New programme |
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 |
New programme |
New programme |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Old programme codes |
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Programme description |
A description of the biological macrozoobenthic communities associated with the predominant seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological macrozoobenthic communities associated with the predominant seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological macrozoobenthic communities associated with the predominant seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological macrozoobenthic communities associated with the predominant seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological macrozoobenthic communities associated with the predominant seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological macrozoobenthic communities associated with the predominant seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological macrozoobenthic communities associated with the predominant seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological macrozoobenthic communities associated with the predominant seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological macrozoobenthic communities associated with the predominant seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological macrozoobenthic communities associated with the predominant seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological communities associated with the
coastal soft bottom seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological communities associated with the
coastal soft bottom seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological communities associated with the
coastal soft bottom seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological communities associated with the
coastal soft bottom seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological communities associated with the
coastal soft bottom seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological communities associated with the
coastal soft bottom seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological communities associated with the
coastal soft bottom seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological communities associated with the
coastal soft bottom seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological communities associated with the
coastal soft bottom seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological communities associated with the
coastal soft bottom seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological communities associated with the
coastal soft bottom seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological communities associated with the
coastal soft bottom seabed habitats. Changes in communities and abundance of alien species. |
A description of the biological communities associated with the
coastal soft bottom seabed habitats. Changes in communities and abundance of alien species. |
Coastal hard bottom habitat forming macroalgae and blue mussel communities and population structure of macrozoobenthic species living in these habitats. Aims to observe structure changes in communities, which are especially affected by eutrophication. |
Coastal hard bottom habitat forming macroalgae and blue mussel communities and population structure of macrozoobenthic species living in these habitats. Aims to observe structure changes in communities, which are especially affected by eutrophication. |
Coastal hard bottom habitat forming macroalgae and blue mussel communities and population structure of macrozoobenthic species living in these habitats. Aims to observe structure changes in communities, which are especially affected by eutrophication. |
Coastal hard bottom habitat forming macroalgae and blue mussel communities and population structure of macrozoobenthic species living in these habitats. Aims to observe structure changes in communities, which are especially affected by eutrophication. |
Coastal hard bottom habitat forming macroalgae and blue mussel communities and population structure of macrozoobenthic species living in these habitats. Aims to observe structure changes in communities, which are especially affected by eutrophication. |
Coastal hard bottom habitat forming macroalgae and blue mussel communities and population structure of macrozoobenthic species living in these habitats. Aims to observe structure changes in communities, which are especially affected by eutrophication. |
Program monitors changes in macrophyte community (number of species and species coverage) in soft bottoms in coastal and shallow bay areas, which are affected among other things by eutrophication. |
Program monitors changes in macrophyte community (number of species and species coverage) in soft bottoms in coastal and shallow bay areas, which are affected among other things by eutrophication. |
Program monitors changes in macrophyte community (number of species and species coverage) in soft bottoms in coastal and shallow bay areas, which are affected among other things by eutrophication. |
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 |
Monitoring of the population dynamics, natural and actual range and status of grey seal and ringed seal. Abundance monitoring is conducted from aircraft. Seal bycatch data is collected from fishermen, which describes human pressure on seal mortality. |
Monitoring of the population dynamics, natural and actual range and status of grey seal and ringed seal. Abundance monitoring is conducted from aircraft. Seal bycatch data is collected from fishermen, which describes human pressure on seal mortality. |
Each year, the sub-programme monitors the age and sex structure, reproductive efficiency and health status of seal populations, in particular the nutritional status. Samples are collected from seals caught/recovered by-catches by hunters and fishermen. Most of the samples come from hunted seals.
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Each year, the sub-programme monitors the age and sex structure, reproductive efficiency and health status of seal populations, in particular the nutritional status. Samples are collected from seals caught/recovered by-catches by hunters and fishermen. Most of the samples come from hunted seals.
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The sub-programme monitors the presence of porpoise in Finnish territorial waters by acoustic methods in the North Baltic and Ã
land Seas, where the species is regularly present. This information is complemented by public perceptions. In addition, data are collected on the number of porpoises killed in traps, which illustrates the human impact on porpoise mortality. The objective is to collect data on the Baltic porpoise population as part of international cooperation to preserve the harbour porpoise population classified as critically endangered in the main basin.
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The sub-programme monitors the presence of porpoise in Finnish territorial waters by acoustic methods in the North Baltic and Ã
land Seas, where the species is regularly present. This information is complemented by public perceptions. In addition, data are collected on the number of porpoises killed in traps, which illustrates the human impact on porpoise mortality. The objective is to collect data on the Baltic porpoise population as part of international cooperation to preserve the harbour porpoise population classified as critically endangered in the main basin.
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Zooplankton species composition, abundance and biomass |
Zooplankton species composition, abundance and biomass |
Zooplankton species composition, abundance and biomass |
Zooplankton species composition, abundance and biomass |
Zooplankton species composition, abundance and biomass |
Zooplankton species composition, abundance and biomass |
Phytoplankton species composition, abundance and biomass are monitored by counting phytoplankton from preserved water samples to identify changes in phytoplankton communities (e.g. harmful and invasive species |
Phytoplankton species composition, abundance and biomass are monitored by counting phytoplankton from preserved water samples to identify changes in phytoplankton communities (e.g. harmful and invasive species |
Phytoplankton species composition, abundance and biomass are monitored by counting phytoplankton from preserved water samples to identify changes in phytoplankton communities (e.g. harmful and invasive species |
Phytoplankton species composition, abundance and biomass are monitored by counting phytoplankton from preserved water samples to identify changes in phytoplankton communities (e.g. harmful and invasive species |
Phytoplankton species composition, abundance and biomass are monitored by counting phytoplankton from preserved water samples to identify changes in phytoplankton communities (e.g. harmful and invasive species |
Phytoplankton species composition, abundance and biomass are monitored by counting phytoplankton from preserved water samples to identify changes in phytoplankton communities (e.g. harmful and invasive species |
The sub-programme provides information on fisheries in EU countries. Data on the fish stock is collected by means of fishing samples and sonars. The aim is to provide information, inter alia, on scientific analysis and advice in support of the Common Fisheries Policy.
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The sub-programme provides information on fisheries in EU countries. Data on the fish stock is collected by means of fishing samples and sonars. The aim is to provide information, inter alia, on scientific analysis and advice in support of the Common Fisheries Policy.
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The sub-programme provides information on fisheries in EU countries. Data on the fish stock is collected by means of fishing samples and sonars. The aim is to provide information, inter alia, on scientific analysis and advice in support of the Common Fisheries Policy.
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The sub-programme provides information on fisheries in EU countries. Data on the fish stock is collected by means of fishing samples and sonars. The aim is to provide information, inter alia, on scientific analysis and advice in support of the Common Fisheries Policy.
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The sub-programme provides information on fisheries in EU countries. Data on the fish stock is collected by means of fishing samples and sonars. The aim is to provide information, inter alia, on scientific analysis and advice in support of the Common Fisheries Policy.
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The sub-programme provides information on fisheries in EU countries. Data on the fish stock is collected by means of fishing samples and sonars. The aim is to provide information, inter alia, on scientific analysis and advice in support of the Common Fisheries Policy.
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The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
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The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
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The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
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The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
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The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
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The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
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The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
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The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
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The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
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The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
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The sub-programme monitors catches by commercial fishermen and by-catches of birds and mammals. Monitoring shall be based on periodic catch reports from commercial fishermen to the authorities.
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Program monitors phytoplankton blooms by monitoring pigments. Program produces information on consequences of eutrophication |
Program monitors phytoplankton blooms by monitoring pigments. Program produces information on consequences of eutrophication |
Program monitors phytoplankton blooms by monitoring pigments. Program produces information on consequences of eutrophication |
Program monitors phytoplankton blooms by monitoring pigments. Program produces information on consequences of eutrophication |
Mass mortalities of breeding sea birds are monitored in the vicinity of breeding colonies. Therefore the monitoring is focuses on islands and islets in coastal and territorial waters. Aim is to register number of mass mortality's and causes |
Mass mortalities of breeding sea birds are monitored in the vicinity of breeding colonies. Therefore the monitoring is focuses on islands and islets in coastal and territorial waters. Aim is to register number of mass mortality's and causes |
Hunting of sea birds and seals is practiced in coastal and territorial waters according to hunting regulations.Hunting organizations carry out game questionnaires. Hunting statistics are maintained by the hunting organizations and stored into a database. Data on species requiring special permit is obtained through the licensing system. |
Hunting of sea birds and seals is practiced in coastal and territorial waters according to hunting regulations.Hunting organizations carry out game questionnaires. Hunting statistics are maintained by the hunting organizations and stored into a database. Data on species requiring special permit is obtained through the licensing system. |
Hunting of sea birds and seals is practiced in coastal and territorial waters according to hunting regulations.Hunting organizations carry out game questionnaires. Hunting statistics are maintained by the hunting organizations and stored into a database. Data on species requiring special permit is obtained through the licensing system. |
Hunting of sea birds and seals is practiced in coastal and territorial waters according to hunting regulations.Hunting organizations carry out game questionnaires. Hunting statistics are maintained by the hunting organizations and stored into a database. Data on species requiring special permit is obtained through the licensing system. |
Monitoring purpose |
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Other policies and conventions |
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Regional cooperation - coordinating body |
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Regional cooperation - countries involved |
DE,DK,EE,LT,LV,PL,SE |
DE,DK,EE,LT,LV,PL,SE |
DE,DK,EE,LT,LV,PL,SE |
DE,DK,EE,LT,LV,PL,SE |
DE,DK,EE,LT,LV,PL,SE |
DE,DK,EE,LT,LV,PL,SE |
DE,DK,EE,LT,LV,PL,SE |
DE,DK,EE,LT,LV,PL,SE |
DE,DK,EE,LT,LV,PL,SE |
DE,DK,EE,LT,LV,PL,SE |
EE,SE |
EE,SE |
EE,SE |
EE,SE |
EE,SE |
EE,SE |
EE,SE |
EE,SE |
EE,SE |
EE,SE |
EE,SE |
EE,SE |
EE,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 |
DE,DK,EE,LT,LV,PL,SE |
DE,DK,EE,LT,LV,PL,SE |
DE,DK,EE,LT,LV,PL,SE |
SE |
SE |
DE,DK,PL,SE |
DE,DK,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 |
DE,DK,EE,LT,LV,PL,SE |
DE,DK,EE,LT,LV,SE |
DE,DK,EE,LT,LV,SE |
DE,DK,EE,LT,LV,SE |
DE,DK,EE,LT,LV,SE |
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Regional cooperation - implementation level |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
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 |
Agreed data collection methods |
Agreed data collection methods |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
Common monitoring strategy |
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 |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Agreed data collection methods |
Agreed data collection methods |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
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 |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
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Monitoring details |
Essential information describing this national sub-programme is available in the HELCOM COMBINE manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna. |
Essential information describing this national sub-programme is available in the HELCOM COMBINE manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna. |
Essential information describing this national sub-programme is available in the HELCOM COMBINE manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna. |
Essential information describing this national sub-programme is available in the HELCOM COMBINE manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna. |
Essential information describing this national sub-programme is available in the HELCOM COMBINE manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna. |
Essential information describing this national sub-programme is available in the HELCOM COMBINE manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna. |
Essential information describing this national sub-programme is available in the HELCOM COMBINE manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna. |
Essential information describing this national sub-programme is available in the HELCOM COMBINE manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna. |
Essential information describing this national sub-programme is available in the HELCOM COMBINE manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna. |
Essential information describing this national sub-programme is available in the HELCOM COMBINE manual: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna. |
Monitoring is part of the EU Water Framework Directive monitoring of coastal waters. Ref: Mountain et al. (Sampling of soft benthic animals and sediment for VPD monitoring in coastal waters. In: Mountain et al. (ed.) organisation of biological monitoring and acquisition of analyses for river basin management areas. 35 reports from the Finnish Environment Institute, Annex 4.
The method also followed essentially the HELCOM Combine: Https://www.helcom.fi/wp-content/uploads/2019/08/Manual-for-Marine-Monitoring-in-the-COMBINE-Programme-of-HELCOM_PartC_AnnexC8.pdf
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Monitoring is part of the EU Water Framework Directive monitoring of coastal waters. Ref: Mountain et al. (Sampling of soft benthic animals and sediment for VPD monitoring in coastal waters. In: Mountain et al. (ed.) organisation of biological monitoring and acquisition of analyses for river basin management areas. 35 reports from the Finnish Environment Institute, Annex 4.
The method also followed essentially the HELCOM Combine: Https://www.helcom.fi/wp-content/uploads/2019/08/Manual-for-Marine-Monitoring-in-the-COMBINE-Programme-of-HELCOM_PartC_AnnexC8.pdf
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Monitoring is part of the EU Water Framework Directive monitoring of coastal waters. Ref: Mountain et al. (Sampling of soft benthic animals and sediment for VPD monitoring in coastal waters. In: Mountain et al. (ed.) organisation of biological monitoring and acquisition of analyses for river basin management areas. 35 reports from the Finnish Environment Institute, Annex 4.
The method also followed essentially the HELCOM Combine: Https://www.helcom.fi/wp-content/uploads/2019/08/Manual-for-Marine-Monitoring-in-the-COMBINE-Programme-of-HELCOM_PartC_AnnexC8.pdf
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Monitoring is part of the EU Water Framework Directive monitoring of coastal waters. Ref: Mountain et al. (Sampling of soft benthic animals and sediment for VPD monitoring in coastal waters. In: Mountain et al. (ed.) organisation of biological monitoring and acquisition of analyses for river basin management areas. 35 reports from the Finnish Environment Institute, Annex 4.
The method also followed essentially the HELCOM Combine: Https://www.helcom.fi/wp-content/uploads/2019/08/Manual-for-Marine-Monitoring-in-the-COMBINE-Programme-of-HELCOM_PartC_AnnexC8.pdf
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Monitoring is part of the EU Water Framework Directive monitoring of coastal waters. Ref: Mountain et al. (Sampling of soft benthic animals and sediment for VPD monitoring in coastal waters. In: Mountain et al. (ed.) organisation of biological monitoring and acquisition of analyses for river basin management areas. 35 reports from the Finnish Environment Institute, Annex 4.
The method also followed essentially the HELCOM Combine: Https://www.helcom.fi/wp-content/uploads/2019/08/Manual-for-Marine-Monitoring-in-the-COMBINE-Programme-of-HELCOM_PartC_AnnexC8.pdf
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Monitoring is part of the EU Water Framework Directive monitoring of coastal waters. Ref: Mountain et al. (Sampling of soft benthic animals and sediment for VPD monitoring in coastal waters. In: Mountain et al. (ed.) organisation of biological monitoring and acquisition of analyses for river basin management areas. 35 reports from the Finnish Environment Institute, Annex 4.
The method also followed essentially the HELCOM Combine: Https://www.helcom.fi/wp-content/uploads/2019/08/Manual-for-Marine-Monitoring-in-the-COMBINE-Programme-of-HELCOM_PartC_AnnexC8.pdf
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Monitoring is part of the EU Water Framework Directive monitoring of coastal waters. Ref: Mountain et al. (Sampling of soft benthic animals and sediment for VPD monitoring in coastal waters. In: Mountain et al. (ed.) organisation of biological monitoring and acquisition of analyses for river basin management areas. 35 reports from the Finnish Environment Institute, Annex 4.
The method also followed essentially the HELCOM Combine: Https://www.helcom.fi/wp-content/uploads/2019/08/Manual-for-Marine-Monitoring-in-the-COMBINE-Programme-of-HELCOM_PartC_AnnexC8.pdf
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Monitoring is part of the EU Water Framework Directive monitoring of coastal waters. Ref: Mountain et al. (Sampling of soft benthic animals and sediment for VPD monitoring in coastal waters. In: Mountain et al. (ed.) organisation of biological monitoring and acquisition of analyses for river basin management areas. 35 reports from the Finnish Environment Institute, Annex 4.
The method also followed essentially the HELCOM Combine: Https://www.helcom.fi/wp-content/uploads/2019/08/Manual-for-Marine-Monitoring-in-the-COMBINE-Programme-of-HELCOM_PartC_AnnexC8.pdf
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Monitoring is part of the EU Water Framework Directive monitoring of coastal waters. Ref: Mountain et al. (Sampling of soft benthic animals and sediment for VPD monitoring in coastal waters. In: Mountain et al. (ed.) organisation of biological monitoring and acquisition of analyses for river basin management areas. 35 reports from the Finnish Environment Institute, Annex 4.
The method also followed essentially the HELCOM Combine: Https://www.helcom.fi/wp-content/uploads/2019/08/Manual-for-Marine-Monitoring-in-the-COMBINE-Programme-of-HELCOM_PartC_AnnexC8.pdf
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Monitoring is part of the EU Water Framework Directive monitoring of coastal waters. Ref: Mountain et al. (Sampling of soft benthic animals and sediment for VPD monitoring in coastal waters. In: Mountain et al. (ed.) organisation of biological monitoring and acquisition of analyses for river basin management areas. 35 reports from the Finnish Environment Institute, Annex 4.
The method also followed essentially the HELCOM Combine: Https://www.helcom.fi/wp-content/uploads/2019/08/Manual-for-Marine-Monitoring-in-the-COMBINE-Programme-of-HELCOM_PartC_AnnexC8.pdf
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Monitoring is part of the EU Water Framework Directive monitoring of coastal waters. Ref: Mountain et al. (Sampling of soft benthic animals and sediment for VPD monitoring in coastal waters. In: Mountain et al. (ed.) organisation of biological monitoring and acquisition of analyses for river basin management areas. 35 reports from the Finnish Environment Institute, Annex 4.
The method also followed essentially the HELCOM Combine: Https://www.helcom.fi/wp-content/uploads/2019/08/Manual-for-Marine-Monitoring-in-the-COMBINE-Programme-of-HELCOM_PartC_AnnexC8.pdf
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Monitoring is part of the EU Water Framework Directive monitoring of coastal waters. Ref: Mountain et al. (Sampling of soft benthic animals and sediment for VPD monitoring in coastal waters. In: Mountain et al. (ed.) organisation of biological monitoring and acquisition of analyses for river basin management areas. 35 reports from the Finnish Environment Institute, Annex 4.
The method also followed essentially the HELCOM Combine: Https://www.helcom.fi/wp-content/uploads/2019/08/Manual-for-Marine-Monitoring-in-the-COMBINE-Programme-of-HELCOM_PartC_AnnexC8.pdf
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Monitoring is part of the EU Water Framework Directive monitoring of coastal waters. Ref: Mountain et al. (Sampling of soft benthic animals and sediment for VPD monitoring in coastal waters. In: Mountain et al. (ed.) organisation of biological monitoring and acquisition of analyses for river basin management areas. 35 reports from the Finnish Environment Institute, Annex 4.
The method also followed essentially the HELCOM Combine: Https://www.helcom.fi/wp-content/uploads/2019/08/Manual-for-Marine-Monitoring-in-the-COMBINE-Programme-of-HELCOM_PartC_AnnexC8.pdf
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No monitoring in Bothnian Bay since species monitored do not habitat that area |
No monitoring in Bothnian Bay since species monitored do not habitat that area |
No monitoring in Bothnian Bay since species monitored do not habitat that area |
No monitoring in Bothnian Bay since species monitored do not habitat that area |
No monitoring in Bothnian Bay since species monitored do not habitat that area |
No monitoring in Bothnian Bay since species monitored do not habitat that area |
Diving transects and bathyscope
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Diving transects and bathyscope
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Diving transects and bathyscope
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Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â Live Yearbook 2010: 40-51
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Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â Live Yearbook 2010: 40-51
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Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â Live Yearbook 2010: 40-51
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Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â Live Yearbook 2010: 40-51
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Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â Live Yearbook 2010: 40-51
|
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â Live Yearbook 2010: 40-51
|
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â Live Yearbook 2010: 40-51
|
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â Live Yearbook 2010: 40-51
|
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â Live Yearbook 2010: 40-51
|
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â Live Yearbook 2010: 40-51
|
Rintala J. 2011. Development of Saaristolintu stocks in Finland from 1986 to 2010. â 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
|
FINLAND: https://www.luke.fi/tietoa-luonnonvaroista/riista/hylkeet/hylkeiden-kanta-arvioinnin-menetelmat/.
HELCOM: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/seals-abundance |
FINLAND: https://www.luke.fi/tietoa-luonnonvaroista/riista/hylkeet/hylkeiden-kanta-arvioinnin-menetelmat/.
HELCOM: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/seals-abundance |
FINLAND: https://www.luke.fi/tietoa-luonnonvaroista/riista/hylkeet/hylkeiden-kanta-arvioinnin-menetelmat/
HELCOM: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/health-status. |
FINLAND: https://www.luke.fi/tietoa-luonnonvaroista/riista/hylkeet/hylkeiden-kanta-arvioinnin-menetelmat/
HELCOM: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/health-status. |
Acoustic monitoring and sightings by citizens.
Citizen sightings were coherently collected since 2001, pilot monitoring was started in 2011-2013 and the national monitoring started in 2016. |
Acoustic monitoring and sightings by citizens.
Citizen sightings were coherently collected since 2001, pilot monitoring was started in 2011-2013 and the national monitoring started in 2016. |
Program follows HELCOM Combine - https://helcom.fi/media/publications/Guidelines-for-monitoring-of-mesozooplankton.pdf |
Program follows HELCOM Combine - https://helcom.fi/media/publications/Guidelines-for-monitoring-of-mesozooplankton.pdf |
Program follows HELCOM Combine - https://helcom.fi/media/publications/Guidelines-for-monitoring-of-mesozooplankton.pdf |
Program follows HELCOM Combine - https://helcom.fi/media/publications/Guidelines-for-monitoring-of-mesozooplankton.pdf |
Program follows HELCOM Combine - https://helcom.fi/media/publications/Guidelines-for-monitoring-of-mesozooplankton.pdf |
Program follows HELCOM Combine - https://helcom.fi/media/publications/Guidelines-for-monitoring-of-mesozooplankton.pdf |
Samples are taken onboard research vessels under the coastal monitoring (part of EU WFD) and offshore monitoring. |
Samples are taken onboard research vessels under the coastal monitoring (part of EU WFD) and offshore monitoring. |
Samples are taken onboard research vessels under the coastal monitoring (part of EU WFD) and offshore monitoring. |
Samples are taken onboard research vessels under the coastal monitoring (part of EU WFD) and offshore monitoring. |
Samples are taken onboard research vessels under the coastal monitoring (part of EU WFD) and offshore monitoring. |
Samples are taken onboard research vessels under the coastal monitoring (part of EU WFD) and offshore monitoring. |
Fishermensâ reporting to authorities.
|
Fishermensâ reporting to authorities.
|
Fishermensâ reporting to authorities.
|
Fishermensâ reporting to authorities.
|
Fishermensâ reporting to authorities.
|
Fishermensâ reporting to authorities.
|
Fishermensâ reporting to authorities.
|
Fishermensâ reporting to authorities.
|
Fishermensâ reporting to authorities.
|
Fishermensâ reporting to authorities.
|
Fishermensâ 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, âpassiveâ 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, âpassiveâ monitoring, i.e. information obtained through other activities and monitoring.
|
||||||||||||||
Features |
Shelf ecosystems
|
Shelf ecosystems
|
Eutrophication
|
Benthic broad habitats
|
Chemical characteristics
|
Chemical characteristics
|
Chemical characteristics
|
Chemical characteristics
|
Physical and hydrological characteristics
|
Physical and hydrological characteristics
|
Physical and hydrological characteristics
|
Shelf ecosystems
|
Physical and hydrological characteristics
|
Shelf ecosystems
|
Eutrophication
|
Benthic broad habitats
|
Benthic broad habitats
|
Chemical characteristics
|
Chemical characteristics
|
Chemical characteristics
|
Chemical characteristics
|
Physical and hydrological characteristics
|
Physical and hydrological characteristics
|
Newly introduced non-indigenous species
|
Established non-indigenous species
|
Eutrophication
|
Eutrophication
|
Benthic broad habitats
|
Benthic broad habitats
|
Eutrophication
|
Eutrophication
|
Benthic broad habitats
|
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
|
Seals
|
Seals
|
Seals
|
Adverse effects on species or habitats
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Pelagic broad habitats
|
Newly introduced non-indigenous species
|
Established non-indigenous species
|
Shelf ecosystems
|
Shelf ecosystems
|
Shelf ecosystems
|
Pelagic broad habitats
|
Newly introduced non-indigenous species
|
Shelf ecosystems
|
Shelf ecosystems
|
Eutrophication
|
Eutrophication
|
Pelagic shelf fish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
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)
|
Shelf ecosystems
|
Shelf ecosystems
|
Eutrophication
|
Eutrophication
|
Pelagic-feeding birds
|
Surface-feeding birds
|
Benthic-feeding birds
|
Grazing birds
|
Pelagic-feeding birds
|
Seals
|
Shelf ecosystems
|
Shelf ecosystems
|
Eutrophication
|
Benthic broad habitats
|
Chemical characteristics
|
Chemical characteristics
|
Chemical characteristics
|
Chemical characteristics
|
Physical and hydrological characteristics
|
Physical and hydrological characteristics
|
Physical and hydrological characteristics
|
Shelf ecosystems
|
Physical and hydrological characteristics
|
Shelf ecosystems
|
Eutrophication
|
Benthic broad habitats
|
Benthic broad habitats
|
Chemical characteristics
|
Chemical characteristics
|
Chemical characteristics
|
Chemical characteristics
|
Physical and hydrological characteristics
|
Physical and hydrological characteristics
|
Newly introduced non-indigenous species
|
Established non-indigenous species
|
Eutrophication
|
Eutrophication
|
Benthic broad habitats
|
Benthic broad habitats
|
Eutrophication
|
Eutrophication
|
Benthic broad habitats
|
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
|
Seals
|
Seals
|
Seals
|
Adverse effects on species or habitats
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Pelagic broad habitats
|
Newly introduced non-indigenous species
|
Established non-indigenous species
|
Shelf ecosystems
|
Shelf ecosystems
|
Shelf ecosystems
|
Pelagic broad habitats
|
Newly introduced non-indigenous species
|
Shelf ecosystems
|
Shelf ecosystems
|
Eutrophication
|
Eutrophication
|
Pelagic shelf fish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
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)
|
Shelf ecosystems
|
Shelf ecosystems
|
Eutrophication
|
Eutrophication
|
Pelagic-feeding birds
|
Surface-feeding birds
|
Benthic-feeding birds
|
Grazing birds
|
Pelagic-feeding birds
|
Seals
|
|
Shelf ecosystems
|
Shelf ecosystems
|
Eutrophication
|
Benthic broad habitats
|
Chemical characteristics
|
Chemical characteristics
|
Chemical characteristics
|
Chemical characteristics
|
Physical and hydrological characteristics
|
Physical and hydrological characteristics
|
Physical and hydrological characteristics
|
Shelf ecosystems
|
Physical and hydrological characteristics
|
Shelf ecosystems
|
Eutrophication
|
Benthic broad habitats
|
Benthic broad habitats
|
Chemical characteristics
|
Chemical characteristics
|
Chemical characteristics
|
Chemical characteristics
|
Physical and hydrological characteristics
|
Physical and hydrological characteristics
|
Newly introduced non-indigenous species
|
Established non-indigenous species
|
Eutrophication
|
Eutrophication
|
Benthic broad habitats
|
Benthic broad habitats
|
Eutrophication
|
Eutrophication
|
Benthic broad habitats
|
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
|
Seals
|
Seals
|
Seals
|
Adverse effects on species or habitats
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Pelagic broad habitats
|
Newly introduced non-indigenous species
|
Established non-indigenous species
|
Shelf ecosystems
|
Shelf ecosystems
|
Shelf ecosystems
|
Pelagic broad habitats
|
Newly introduced non-indigenous species
|
Shelf ecosystems
|
Shelf ecosystems
|
Eutrophication
|
Eutrophication
|
Pelagic shelf fish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
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)
|
Shelf ecosystems
|
Shelf ecosystems
|
Eutrophication
|
Eutrophication
|
Pelagic-feeding birds
|
Surface-feeding birds
|
Benthic-feeding birds
|
Grazing birds
|
Pelagic-feeding birds
|
Seals
|
|
Shelf ecosystems
|
Shelf ecosystems
|
Eutrophication
|
Benthic broad habitats
|
Chemical characteristics
|
Chemical characteristics
|
Chemical characteristics
|
Chemical characteristics
|
Physical and hydrological characteristics
|
Physical and hydrological characteristics
|
Physical and hydrological characteristics
|
Shelf ecosystems
|
Physical and hydrological characteristics
|
Shelf ecosystems
|
Eutrophication
|
Benthic broad habitats
|
Benthic broad habitats
|
Chemical characteristics
|
Chemical characteristics
|
Chemical characteristics
|
Chemical characteristics
|
Physical and hydrological characteristics
|
Physical and hydrological characteristics
|
Newly introduced non-indigenous species
|
Established non-indigenous species
|
Eutrophication
|
Eutrophication
|
Benthic broad habitats
|
Benthic broad habitats
|
Eutrophication
|
Eutrophication
|
Benthic broad habitats
|
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
|
Seals
|
Seals
|
Seals
|
Adverse effects on species or habitats
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Pelagic broad habitats
|
Newly introduced non-indigenous species
|
Established non-indigenous species
|
Shelf ecosystems
|
Shelf ecosystems
|
Shelf ecosystems
|
Pelagic broad habitats
|
Newly introduced non-indigenous species
|
Shelf ecosystems
|
Shelf ecosystems
|
Eutrophication
|
Eutrophication
|
Pelagic shelf fish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
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)
|
Shelf ecosystems
|
Shelf ecosystems
|
Eutrophication
|
Eutrophication
|
Pelagic-feeding birds
|
Surface-feeding birds
|
Benthic-feeding birds
|
Grazing birds
|
Pelagic-feeding birds
|
Seals
|
|
Elements |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
GES criteria |
D4C2 |
D4C3 |
D5C8 |
D6C5 |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
D4C1 |
D4C1 |
D4C2 |
D4C2 |
D5C8 |
D6C5 |
D7C2 |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
D2C1 |
D2C2 |
D5C6 |
D5C7 |
D6C5 |
D6C5 |
D5C6 |
D5C7 |
D6C5 |
D1C1 |
D1C2 |
D1C2 |
D1C2 |
D1C2 |
D1C2 |
D1C4 |
D1C4 |
D1C4 |
D1C4 |
D1C4 |
D1C2 |
D1C2 |
D1C2 |
D1C2 |
D1C4 |
D1C4 |
D1C4 |
D1C4 |
D1C2 |
D1C3 |
D4C4 |
D8C2 |
D1C2 |
D1C4 |
D1C3 |
NotRelevan |
D1C2 |
D1C4 |
D1C6 |
D2C1 |
D2C2 |
D4C1 |
D4C2 |
D4C3 |
D1C6 |
D2C1 |
D4C1 |
D4C2 |
D5C3 |
D5C3 |
D1C2 |
D3C1 |
D3C2 |
D3C2 |
D3C3 |
D3C3 |
D1C1 |
D1C1 |
D1C1 |
D1C1 |
D1C1 |
D3C1 |
D3C2 |
D3C3 |
D4C1 |
D4C2 |
NotRelevan |
D4C2 |
D4C4 |
D5C2 |
D5C3 |
D1C3 |
D1C3 |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
Parameters |
|
|
|
|
|
|
|
|
|
|
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|
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|
|
|
Parameter Other |
biomass; species richness |
Species richness; abundance; biomass; length |
See SYKE manual |
Species diversity |
Number of species |
Number of species |
Biomass; Species richness |
Species richness; Abundance; Biomass |
Species richness; Abundance; Biomass |
See SYKE manual |
Abundance |
Abundance |
Maximum depth limit and coverage of Mytilus trossu |
Diversity of macrofauna on fucus; Macroalgae cover |
Coverage % on macrophytes |
Species richness |
Blubber thickness |
Biomass; Abundance |
Diversity |
Abundance; Species richness |
Species richness; Diversity |
Ratio of Diatoms & Dinoflagellates |
Ratio of Diatoms & Dinoflagellates |
Number of spawning individuals; Number of smolts |
Number of spawning individuals; Number of smolts |
Age |
age |
age |
age |
Abundance of Cyprinidae |
Abundance of Cyprinidae |
Fishing effort (days) |
Biomass |
Mortality |
Mortality |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Spatial scope |
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Marine reporting units |
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Temporal scope (start date - end date) |
1964-9999 |
1964-9999 |
1964-9999 |
1964-9999 |
1964-9999 |
1964-9999 |
1964-9999 |
1964-9999 |
1964-9999 |
1964-9999 |
1964-9999 |
1964-9999 |
1964-9999 |
1964-9999 |
1964-9999 |
1964-9999 |
1964-9999 |
1964-9999 |
1964-9999 |
1964-9999 |
1964-9999 |
1964-9999 |
1964-9999 |
1993-9999 |
1993-9999 |
1993-9999 |
1993-9999 |
1993-9999 |
1993-9999 |
2020-9999 |
2020-9999 |
2020-9999 |
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 |
1988-9999 |
1988-9999 |
1998-9999 |
1998-9999 |
2001-9999 |
2001-9999 |
1979-9999 |
1979-9999 |
1979-9999 |
1979-9999 |
1979-9999 |
1979-9999 |
1979-9999 |
1979-9999 |
1979-9999 |
1979-9999 |
1979-9999 |
1979-9999 |
2002-9999 |
2002-9999 |
2002-9999 |
2002-9999 |
2002-9999 |
2002-9999 |
1980-9999 |
1980-9999 |
1980-9999 |
1980-9999 |
1980-9999 |
1980-9999 |
1980-9999 |
1980-9999 |
1980-9999 |
1980-9999 |
1980-9999 |
1979-9999 |
1979-9999 |
1979-9999 |
1979-9999 |
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 |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
3-yearly |
3-yearly |
3-yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Continually |
Continually |
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 |
Continually |
Continually |
Continually |
Continually |
Other |
Other |
Continually |
Continually |
Continually |
Continually |
Monitoring type |
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Monitoring method |
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Monitoring method other |
Bladder wrack and macroalgae monitoring follows Finnish Environment Institutes monitoring instructions, which follows HELCOM COMBINE - https://helcom.fi/wp-content/uploads/2019/08/Manual-for-Marine-Monitoring-in-the-COMBINE-Programme-of-HELCOM_PartC_AnnexC9.pdf.
Blue mussel monitoring follows bladder wrack monitoring instructions. |
Bladder wrack and macroalgae monitoring follows Finnish Environment Institutes monitoring instructions, which follows HELCOM COMBINE - https://helcom.fi/wp-content/uploads/2019/08/Manual-for-Marine-Monitoring-in-the-COMBINE-Programme-of-HELCOM_PartC_AnnexC9.pdf.
Blue mussel monitoring follows bladder wrack monitoring instructions. |
Bladder wrack and macroalgae monitoring follows Finnish Environment Institutes monitoring instructions, which follows HELCOM COMBINE - https://helcom.fi/wp-content/uploads/2019/08/Manual-for-Marine-Monitoring-in-the-COMBINE-Programme-of-HELCOM_PartC_AnnexC9.pdf.
Blue mussel monitoring follows bladder wrack monitoring instructions. |
Bladder wrack and macroalgae monitoring follows Finnish Environment Institutes monitoring instructions, which follows HELCOM COMBINE - https://helcom.fi/wp-content/uploads/2019/08/Manual-for-Marine-Monitoring-in-the-COMBINE-Programme-of-HELCOM_PartC_AnnexC9.pdf.
Blue mussel monitoring follows bladder wrack monitoring instructions. |
Bladder wrack and macroalgae monitoring follows Finnish Environment Institutes monitoring instructions, which follows HELCOM COMBINE - https://helcom.fi/wp-content/uploads/2019/08/Manual-for-Marine-Monitoring-in-the-COMBINE-Programme-of-HELCOM_PartC_AnnexC9.pdf.
Blue mussel monitoring follows bladder wrack monitoring instructions. |
Bladder wrack and macroalgae monitoring follows Finnish Environment Institutes monitoring instructions, which follows HELCOM COMBINE - https://helcom.fi/wp-content/uploads/2019/08/Manual-for-Marine-Monitoring-in-the-COMBINE-Programme-of-HELCOM_PartC_AnnexC9.pdf.
Blue mussel monitoring follows bladder wrack monitoring instructions. |
The Finnish Inventory Programme for the Underwater Marine Environment (VELMU) - https://www.environment.fi/en-US/VELMU
Åbo Akademi - http://urn.fi/URN:ISBN:978-952-12-3309-8 |
The Finnish Inventory Programme for the Underwater Marine Environment (VELMU) - https://www.environment.fi/en-US/VELMU
Åbo Akademi - http://urn.fi/URN:ISBN:978-952-12-3309-8 |
The Finnish Inventory Programme for the Underwater Marine Environment (VELMU) - https://www.environment.fi/en-US/VELMU
Åbo Akademi - http://urn.fi/URN:ISBN:978-952-12-3309-8 |
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 |
HELCOM:n asiantuntijaryhmä kehittää parhaillaan koko Itämeren kattavaa indikaattoria ”Abundance and distribution of harbour porpoises”. Tämän indikaattorin kynnysarvoja hyvälle tilalle tai mahdollisia alaindikaattoreita ei ole vielä määritelty, mutta kansalliset merenhoidon hyvän tilan määritelmät ovat:
• Pyöriäisen levinneisyysalueen reunat ulottuvat Suomen merialueille, pl. Perämeri, ja se havaitaan vuosittain kullakin merialueella (Suomenlahti, Pohjois-Itämeri, Selkämeri, Merenkurkku, Saaristomeri ja Ahvenanmeri).
• Pyöriäisen populaation tulisi kasvaa Itämeren pääaltaalla kohti elinvoimaista populaatiokokoa. |
HELCOM:n asiantuntijaryhmä kehittää parhaillaan koko Itämeren kattavaa indikaattoria ”Abundance and distribution of harbour porpoises”. Tämän indikaattorin kynnysarvoja hyvälle tilalle tai mahdollisia alaindikaattoreita ei ole vielä määritelty, mutta kansalliset merenhoidon hyvän tilan määritelmät ovat:
• Pyöriäisen levinneisyysalueen reunat ulottuvat Suomen merialueille, pl. Perämeri, ja se havaitaan vuosittain kullakin merialueella (Suomenlahti, Pohjois-Itämeri, Selkämeri, Merenkurkku, Saaristomeri ja Ahvenanmeri).
• Pyöriäisen populaation tulisi kasvaa Itämeren pääaltaalla kohti elinvoimaista populaatiokokoa. |
Data collection and handling is coordinated in RCB Baltic group and ICES working groups WGBIFS and WGBAST |
Data collection and handling is coordinated in RCB Baltic group and ICES working groups WGBIFS and WGBAST |
Data collection and handling is coordinated in RCB Baltic group and ICES working groups WGBIFS and WGBAST |
Data collection and handling is coordinated in RCB Baltic group and ICES working groups WGBIFS and WGBAST |
Data collection and handling is coordinated in RCB Baltic group and ICES working groups WGBIFS and WGBAST |
Data collection and handling is coordinated in RCB Baltic group and ICES working groups WGBIFS and WGBAST |
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 |
https://helcom.fi/media/documents/Water-column-habitats-Pigments.pdf |
https://helcom.fi/media/documents/Water-column-habitats-Pigments.pdf |
https://helcom.fi/media/documents/Water-column-habitats-Pigments.pdf |
https://helcom.fi/media/documents/Water-column-habitats-Pigments.pdf |
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. |
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Quality control |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
Soft bottom sediment monitoring is FINAS-accredited (SFS-EN ISO/IEC 17025) and follows HELCOM COMBINE manual. |
HELCOM manual for monitoring in COMBINE: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/hardbottom-species |
HELCOM manual for monitoring in COMBINE: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/hardbottom-species |
HELCOM manual for monitoring in COMBINE: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/hardbottom-species |
HELCOM manual for monitoring in COMBINE: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/hardbottom-species |
HELCOM manual for monitoring in COMBINE: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/hardbottom-species |
HELCOM manual for monitoring in COMBINE: http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/hardbottom-species |
Monitoring and methods based on VELMU monitoring
|
Monitoring and methods based on VELMU monitoring
|
Monitoring and methods based on VELMU monitoring
|
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 |
The calculation methods should remain constant. When factors affecting the visibility of seals can be taken into account, the overall population estimates are also reliable. The same methodology is used in all Baltic Sea countries. The stock assessment of the regime is only reliable at the level of the Baltic Sea as a whole. With a more detailed structure, the stock distribution cannot be carried out outside the hair exchange period. Elephant stock assessments and sub-stock allocation are reliable. There are four distinct core areas of occurrence in the Baltic Sea: The Bothnian Sea, the Archipelago Sea, the North Sea of the Gulf of Finland and the Gulf of Riga.
|
The calculation methods should remain constant. When factors affecting the visibility of seals can be taken into account, the overall population estimates are also reliable. The same methodology is used in all Baltic Sea countries. The stock assessment of the regime is only reliable at the level of the Baltic Sea as a whole. With a more detailed structure, the stock distribution cannot be carried out outside the hair exchange period. Elephant stock assessments and sub-stock allocation are reliable. There are four distinct core areas of occurrence in the Baltic Sea: The Bothnian Sea, the Archipelago Sea, the North Sea of the Gulf of Finland and the Gulf of Riga.
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The methodology has been partly harmonised at HELCOM EG MAMA meetings.
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The methodology has been partly harmonised at HELCOM EG MAMA meetings.
|
The acoustic monitoring method used has been proven to be reliable and widely used in other parts of the world and the results are comparable to those carried out in other Baltic Sea countries. All acoustic observations are manually verified. Visual elements shall be interviewed and the reliability of the findings assessed by the expert group before entering them into the databases.
|
The acoustic monitoring method used has been proven to be reliable and widely used in other parts of the world and the results are comparable to those carried out in other Baltic Sea countries. All acoustic observations are manually verified. Visual elements shall be interviewed and the reliability of the findings assessed by the expert group before entering them into the databases.
|
Offshore sampling follows HELCOM COMBINE program and coastal sampling instructions from Finnish Environment Institute (SYKE). Ring tests for zooplankton identifiers (HELCOM ZEN), Inter-and intra-laboratory calibrations. |
Offshore sampling follows HELCOM COMBINE program and coastal sampling instructions from Finnish Environment Institute (SYKE). Ring tests for zooplankton identifiers (HELCOM ZEN), Inter-and intra-laboratory calibrations. |
Offshore sampling follows HELCOM COMBINE program and coastal sampling instructions from Finnish Environment Institute (SYKE). Ring tests for zooplankton identifiers (HELCOM ZEN), Inter-and intra-laboratory calibrations. |
Offshore sampling follows HELCOM COMBINE program and coastal sampling instructions from Finnish Environment Institute (SYKE). Ring tests for zooplankton identifiers (HELCOM ZEN), Inter-and intra-laboratory calibrations. |
Offshore sampling follows HELCOM COMBINE program and coastal sampling instructions from Finnish Environment Institute (SYKE). Ring tests for zooplankton identifiers (HELCOM ZEN), Inter-and intra-laboratory calibrations. |
Offshore sampling follows HELCOM COMBINE program and coastal sampling instructions from Finnish Environment Institute (SYKE). Ring tests for zooplankton identifiers (HELCOM ZEN), Inter-and intra-laboratory calibrations. |
Monitoring follows instructions from Finnish Environment Institute (SYKE), which are based on HELCOM COMBINE program. Certificate of phytoplankton identification is required from person identifying phytoplankton from the sample |
Monitoring follows instructions from Finnish Environment Institute (SYKE), which are based on HELCOM COMBINE program. Certificate of phytoplankton identification is required from person identifying phytoplankton from the sample |
Monitoring follows instructions from Finnish Environment Institute (SYKE), which are based on HELCOM COMBINE program. Certificate of phytoplankton identification is required from person identifying phytoplankton from the sample |
Monitoring follows instructions from Finnish Environment Institute (SYKE), which are based on HELCOM COMBINE program. Certificate of phytoplankton identification is required from person identifying phytoplankton from the sample |
Monitoring follows instructions from Finnish Environment Institute (SYKE), which are based on HELCOM COMBINE program. Certificate of phytoplankton identification is required from person identifying phytoplankton from the sample |
Monitoring follows instructions from Finnish Environment Institute (SYKE), which are based on HELCOM COMBINE program. Certificate of phytoplankton identification is required from person identifying phytoplankton from the sample |
Quality control incorporated to national monitoring |
Quality control incorporated to national monitoring |
Quality control incorporated to national monitoring |
Quality control incorporated to national monitoring |
Quality control incorporated to national monitoring |
Quality control incorporated to national monitoring |
Quality control - https://stat.luke.fi/en/commercial-marine-fishery |
Quality control - https://stat.luke.fi/en/commercial-marine-fishery |
Quality control - https://stat.luke.fi/en/commercial-marine-fishery |
Quality control - https://stat.luke.fi/en/commercial-marine-fishery |
Quality control - https://stat.luke.fi/en/commercial-marine-fishery |
Quality control â https://stat.luke.fi/en/commercial-marine-fishery
|
Quality control - https://stat.luke.fi/en/commercial-marine-fishery |
Quality control - https://stat.luke.fi/en/commercial-marine-fishery |
Quality control - https://stat.luke.fi/en/commercial-marine-fishery |
Quality control - https://stat.luke.fi/en/commercial-marine-fishery |
Quality control - https://stat.luke.fi/en/commercial-marine-fishery |
Fluorometers are calibrated annually in laboratory against standards. Analysis procedure is audited annually by FINAS laboratory accreditation |
Fluorometers are calibrated annually in laboratory against standards. Analysis procedure is audited annually by FINAS laboratory accreditation |
Fluorometers are calibrated annually in laboratory against standards. Analysis procedure is audited annually by FINAS laboratory accreditation |
Fluorometers are calibrated annually in laboratory against standards. Analysis procedure is audited annually by FINAS laboratory accreditation |
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
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https://stat.luke.fi/tilasto/4428/laatuseloste/4697
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https://stat.luke.fi/tilasto/4428/laatuseloste/4697
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https://stat.luke.fi/tilasto/4428/laatuseloste/4697
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Data management |
SYKE's POHJE database (https://www.syke.fi/avointieto).
The same data is submitted to ICES HELCOM database.
HELCOM publishes the indicator data and results: http://metadata.helcom.fi/geonetwork/srv/eng/catalog.search#/metadata/0fdc6cb9-fa15-4ba3-9d73-8aeddb5cff64. |
SYKE's POHJE database (https://www.syke.fi/avointieto).
The same data is submitted to ICES HELCOM database.
HELCOM publishes the indicator data and results: http://metadata.helcom.fi/geonetwork/srv/eng/catalog.search#/metadata/0fdc6cb9-fa15-4ba3-9d73-8aeddb5cff64. |
SYKE's POHJE database (https://www.syke.fi/avointieto).
The same data is submitted to ICES HELCOM database.
HELCOM publishes the indicator data and results: http://metadata.helcom.fi/geonetwork/srv/eng/catalog.search#/metadata/0fdc6cb9-fa15-4ba3-9d73-8aeddb5cff64. |
SYKE's POHJE database (https://www.syke.fi/avointieto).
The same data is submitted to ICES HELCOM database.
HELCOM publishes the indicator data and results: http://metadata.helcom.fi/geonetwork/srv/eng/catalog.search#/metadata/0fdc6cb9-fa15-4ba3-9d73-8aeddb5cff64. |
SYKE's POHJE database (https://www.syke.fi/avointieto).
The same data is submitted to ICES HELCOM database.
HELCOM publishes the indicator data and results: http://metadata.helcom.fi/geonetwork/srv/eng/catalog.search#/metadata/0fdc6cb9-fa15-4ba3-9d73-8aeddb5cff64. |
SYKE's POHJE database (https://www.syke.fi/avointieto).
The same data is submitted to ICES HELCOM database.
HELCOM publishes the indicator data and results: http://metadata.helcom.fi/geonetwork/srv/eng/catalog.search#/metadata/0fdc6cb9-fa15-4ba3-9d73-8aeddb5cff64. |
SYKE's POHJE database (https://www.syke.fi/avointieto).
The same data is submitted to ICES HELCOM database.
HELCOM publishes the indicator data and results: http://metadata.helcom.fi/geonetwork/srv/eng/catalog.search#/metadata/0fdc6cb9-fa15-4ba3-9d73-8aeddb5cff64. |
SYKE's POHJE database (https://www.syke.fi/avointieto).
The same data is submitted to ICES HELCOM database.
HELCOM publishes the indicator data and results: http://metadata.helcom.fi/geonetwork/srv/eng/catalog.search#/metadata/0fdc6cb9-fa15-4ba3-9d73-8aeddb5cff64. |
SYKE's POHJE database (https://www.syke.fi/avointieto).
The same data is submitted to ICES HELCOM database.
HELCOM publishes the indicator data and results: http://metadata.helcom.fi/geonetwork/srv/eng/catalog.search#/metadata/0fdc6cb9-fa15-4ba3-9d73-8aeddb5cff64. |
SYKE's POHJE database (https://www.syke.fi/avointieto).
The same data is submitted to ICES HELCOM database.
HELCOM publishes the indicator data and results: http://metadata.helcom.fi/geonetwork/srv/eng/catalog.search#/metadata/0fdc6cb9-fa15-4ba3-9d73-8aeddb5cff64. |
Stored in SYKE's POHJE database. Currently also submitted to ICES and used in the HELCOM indicator. |
Stored in SYKE's POHJE database. Currently also submitted to ICES and used in the HELCOM indicator. |
Stored in SYKE's POHJE database. Currently also submitted to ICES and used in the HELCOM indicator. |
Stored in SYKE's POHJE database. Currently also submitted to ICES and used in the HELCOM indicator. |
Stored in SYKE's POHJE database. Currently also submitted to ICES and used in the HELCOM indicator. |
Stored in SYKE's POHJE database. Currently also submitted to ICES and used in the HELCOM indicator. |
Stored in SYKE's POHJE database. Currently also submitted to ICES and used in the HELCOM indicator. |
Stored in SYKE's POHJE database. Currently also submitted to ICES and used in the HELCOM indicator. |
Stored in SYKE's POHJE database. Currently also submitted to ICES and used in the HELCOM indicator. |
Stored in SYKE's POHJE database. Currently also submitted to ICES and used in the HELCOM indicator. |
Stored in SYKE's POHJE database. Currently also submitted to ICES and used in the HELCOM indicator. |
Stored in SYKE's POHJE database. Currently also submitted to ICES and used in the HELCOM indicator. |
Stored in SYKE's POHJE database. Currently also submitted to ICES and used in the HELCOM indicator. |
Database being constructed for the monitoring data. |
Database being constructed for the monitoring data. |
Database being constructed for the monitoring data. |
Database being constructed for the monitoring data. |
Database being constructed for the monitoring data. |
Database being constructed for the monitoring data. |
Data will be compatible with VELMU-data and stored in Laji-GIS database |
Data will be compatible with VELMU-data and stored in Laji-GIS database |
Data will be compatible with VELMU-data and stored in Laji-GIS database |
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. |
Raw data is only available to researchers.
The seal material shall be available in the Lukeâs comparison database and public viewable and open clustered number data, with an accuracy of 50 km of ICES rectangles. For each rectangle, a multiple of the calculation times the maximum data of the detected halls shall be reported. For elephants (Fael Sea), the original data is in Swedish.
|
Raw data is only available to researchers.
The seal material shall be available in the Lukeâs comparison database and public viewable and open clustered number data, with an accuracy of 50 km of ICES rectangles. For each rectangle, a multiple of the calculation times the maximum data of the detected halls shall be reported. For elephants (Fael Sea), the original data is in Swedish.
|
Raw data not in publicly available.
Data to indicator: http://metadata.helcom.fi/geonetwork/srv/eng/catalog.search#/metadata/106828cf-70af-4e52-b8d2-bc413c387852 |
Raw data not in publicly available.
Data to indicator: http://metadata.helcom.fi/geonetwork/srv/eng/catalog.search#/metadata/106828cf-70af-4e52-b8d2-bc413c387852 |
Acoustic primary data only for researches to use
|
Acoustic primary data only for researches to use
|
Data saved to SYKE data center, National Oceanographic and Atmospheric Administrations (NOAA) plankton database and International Council for the Exploration of the Sea (ICES) data portal. Results can be found from HELCOM indicators |
Data saved to SYKE data center, National Oceanographic and Atmospheric Administrations (NOAA) plankton database and International Council for the Exploration of the Sea (ICES) data portal. Results can be found from HELCOM indicators |
Data saved to SYKE data center, National Oceanographic and Atmospheric Administrations (NOAA) plankton database and International Council for the Exploration of the Sea (ICES) data portal. Results can be found from HELCOM indicators |
Data saved to SYKE data center, National Oceanographic and Atmospheric Administrations (NOAA) plankton database and International Council for the Exploration of the Sea (ICES) data portal. Results can be found from HELCOM indicators |
Data saved to SYKE data center, National Oceanographic and Atmospheric Administrations (NOAA) plankton database and International Council for the Exploration of the Sea (ICES) data portal. Results can be found from HELCOM indicators |
Data saved to SYKE data center, National Oceanographic and Atmospheric Administrations (NOAA) plankton database and International Council for the Exploration of the Sea (ICES) data portal. Results can be found from HELCOM indicators |
Data is saved into Finland's environmental administrations Hertta- data system and submitted to ICES. |
Data is saved into Finland's environmental administrations Hertta- data system and submitted to ICES. |
Data is saved into Finland's environmental administrations Hertta- data system and submitted to ICES. |
Data is saved into Finland's environmental administrations Hertta- data system and submitted to ICES. |
Data is saved into Finland's environmental administrations Hertta- data system and submitted to ICES. |
Data is saved into Finland's environmental administrations Hertta- data system and submitted to ICES. |
National databases and submissions to ICES DATRAS and ICES Acoustic trawl surveys database. |
National databases and submissions to ICES DATRAS and ICES Acoustic trawl surveys database. |
National databases and submissions to ICES DATRAS and ICES Acoustic trawl surveys database. |
National databases and submissions to ICES DATRAS and ICES Acoustic trawl surveys database. |
National databases and submissions to ICES DATRAS and ICES Acoustic trawl surveys database. |
National databases and submissions to ICES DATRAS and ICES Acoustic trawl surveys database. |
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
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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
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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
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Primary data only accessible for researchers
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Data access |
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Related indicator/name |
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Contact |
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna |
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna |
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna |
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna |
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna |
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna |
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna |
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna |
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna |
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/benthic-community-species-distribution-and-abundance/softbottom-fauna |
SYKE open access interface for environmental data |
SYKE open access interface for environmental data |
SYKE open access interface for environmental data |
SYKE open access interface for environmental data |
SYKE open access interface for environmental data |
SYKE open access interface for environmental data |
SYKE open access interface for environmental data |
SYKE open access interface for environmental data |
SYKE open access interface for environmental data |
SYKE open access interface for environmental data |
SYKE open access interface for environmental data |
SYKE open access interface for environmental data |
SYKE open access interface for environmental data |
http://www.helcom.fi/helcom-at-work/groups/state-and-conservation/eg-mama.
https://www.luke.fi/tietoa-luonnonvaroista/riista/hylkeet/ |
http://www.helcom.fi/helcom-at-work/groups/state-and-conservation/eg-mama.
https://www.luke.fi/tietoa-luonnonvaroista/riista/hylkeet/ |
http://www.helcom.fi/baltic-sea-trends/indicators/reproductive-status-of-seals/
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/health-status |
http://www.helcom.fi/baltic-sea-trends/indicators/reproductive-status-of-seals/
http://www.helcom.fi/action-areas/monitoring-and-assessment/monitoring-manual/mammals/health-status |
http://www.helcom.fi/helcom-at-work/groups/state-and-conservation/eg-mama. |
http://www.helcom.fi/helcom-at-work/groups/state-and-conservation/eg-mama. |
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References |
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf
Kvantitatiivinen pohjaeläinnäytteenotto. SYKE/MK Sisäinen menetelmä SA301, modifioitu HELCOM-ohjeistuksesta.
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf
Kvantitatiivinen pohjaeläinnäytteenotto. SYKE/MK Sisäinen menetelmä SA301, modifioitu HELCOM-ohjeistuksesta.
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf
Kvantitatiivinen pohjaeläinnäytteenotto. SYKE/MK Sisäinen menetelmä SA301, modifioitu HELCOM-ohjeistuksesta.
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf
Kvantitatiivinen pohjaeläinnäytteenotto. SYKE/MK Sisäinen menetelmä SA301, modifioitu HELCOM-ohjeistuksesta.
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf
Kvantitatiivinen pohjaeläinnäytteenotto. SYKE/MK Sisäinen menetelmä SA301, modifioitu HELCOM-ohjeistuksesta.
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf
Kvantitatiivinen pohjaeläinnäytteenotto. SYKE/MK Sisäinen menetelmä SA301, modifioitu HELCOM-ohjeistuksesta.
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf
Kvantitatiivinen pohjaeläinnäytteenotto. SYKE/MK Sisäinen menetelmä SA301, modifioitu HELCOM-ohjeistuksesta.
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf
Kvantitatiivinen pohjaeläinnäytteenotto. SYKE/MK Sisäinen menetelmä SA301, modifioitu HELCOM-ohjeistuksesta.
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf
Kvantitatiivinen pohjaeläinnäytteenotto. SYKE/MK Sisäinen menetelmä SA301, modifioitu HELCOM-ohjeistuksesta.
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf
Kvantitatiivinen pohjaeläinnäytteenotto. SYKE/MK Sisäinen menetelmä SA301, modifioitu HELCOM-ohjeistuksesta.
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
Rannikkovesien pehmeiden pohjien eläinyhteisön seurantaan liittyviä menetelmäohjeistuksia:
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
SFS 5076:1989. Water quality. Sampling of the bottom fauna on soft bottoms with an Ekman grab. Vesitutkimukset. Pohjaeläinnäytteenotto Ekman-noutimella pehmeiltä pohjilta.
SFS-EN ISO 10870:2012 Water quality. Guidelines for the selection of sampling methods and devices for benthic macroinvertebrates in fresh waters (ISO 10870:2012)
SFS 5077:1989. Water quality. Handnet sampling of the bottom fauna in running waters. Vesitutkimukset. Pohjaeläinnäytteenotto käsihaavilla virtaavissa vesissä.
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf Lax H-G, Perus J 2008.
Pehmeiden pohjien pohjaeläinten ja sedimentin näytteenotto rannikkovesien VPD-seurannassa. Teoksessa Vuori et al. (toim.) Vesienhoitoalueiden biologisten seurantojen järjestäminen ja määritysten hankinta. Suomen ympäristökeskuksen raportteja 35, liite 4
Nygård H, 2018. Pohjaeläinnäytteenotto rannikkovesialueilla. https://www.ymparisto.fi/download/noname/%7BEAA3550F-CB3C-4359-A05C-975152698BDF%7D/141803
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
Rannikkovesien pehmeiden pohjien eläinyhteisön seurantaan liittyviä menetelmäohjeistuksia:
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
SFS 5076:1989. Water quality. Sampling of the bottom fauna on soft bottoms with an Ekman grab. Vesitutkimukset. Pohjaeläinnäytteenotto Ekman-noutimella pehmeiltä pohjilta.
SFS-EN ISO 10870:2012 Water quality. Guidelines for the selection of sampling methods and devices for benthic macroinvertebrates in fresh waters (ISO 10870:2012)
SFS 5077:1989. Water quality. Handnet sampling of the bottom fauna in running waters. Vesitutkimukset. Pohjaeläinnäytteenotto käsihaavilla virtaavissa vesissä.
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf Lax H-G, Perus J 2008.
Pehmeiden pohjien pohjaeläinten ja sedimentin näytteenotto rannikkovesien VPD-seurannassa. Teoksessa Vuori et al. (toim.) Vesienhoitoalueiden biologisten seurantojen järjestäminen ja määritysten hankinta. Suomen ympäristökeskuksen raportteja 35, liite 4
Nygård H, 2018. Pohjaeläinnäytteenotto rannikkovesialueilla. https://www.ymparisto.fi/download/noname/%7BEAA3550F-CB3C-4359-A05C-975152698BDF%7D/141803
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
Rannikkovesien pehmeiden pohjien eläinyhteisön seurantaan liittyviä menetelmäohjeistuksia:
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
SFS 5076:1989. Water quality. Sampling of the bottom fauna on soft bottoms with an Ekman grab. Vesitutkimukset. Pohjaeläinnäytteenotto Ekman-noutimella pehmeiltä pohjilta.
SFS-EN ISO 10870:2012 Water quality. Guidelines for the selection of sampling methods and devices for benthic macroinvertebrates in fresh waters (ISO 10870:2012)
SFS 5077:1989. Water quality. Handnet sampling of the bottom fauna in running waters. Vesitutkimukset. Pohjaeläinnäytteenotto käsihaavilla virtaavissa vesissä.
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf Lax H-G, Perus J 2008.
Pehmeiden pohjien pohjaeläinten ja sedimentin näytteenotto rannikkovesien VPD-seurannassa. Teoksessa Vuori et al. (toim.) Vesienhoitoalueiden biologisten seurantojen järjestäminen ja määritysten hankinta. Suomen ympäristökeskuksen raportteja 35, liite 4
Nygård H, 2018. Pohjaeläinnäytteenotto rannikkovesialueilla. https://www.ymparisto.fi/download/noname/%7BEAA3550F-CB3C-4359-A05C-975152698BDF%7D/141803
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
Rannikkovesien pehmeiden pohjien eläinyhteisön seurantaan liittyviä menetelmäohjeistuksia:
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
SFS 5076:1989. Water quality. Sampling of the bottom fauna on soft bottoms with an Ekman grab. Vesitutkimukset. Pohjaeläinnäytteenotto Ekman-noutimella pehmeiltä pohjilta.
SFS-EN ISO 10870:2012 Water quality. Guidelines for the selection of sampling methods and devices for benthic macroinvertebrates in fresh waters (ISO 10870:2012)
SFS 5077:1989. Water quality. Handnet sampling of the bottom fauna in running waters. Vesitutkimukset. Pohjaeläinnäytteenotto käsihaavilla virtaavissa vesissä.
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf Lax H-G, Perus J 2008.
Pehmeiden pohjien pohjaeläinten ja sedimentin näytteenotto rannikkovesien VPD-seurannassa. Teoksessa Vuori et al. (toim.) Vesienhoitoalueiden biologisten seurantojen järjestäminen ja määritysten hankinta. Suomen ympäristökeskuksen raportteja 35, liite 4
Nygård H, 2018. Pohjaeläinnäytteenotto rannikkovesialueilla. https://www.ymparisto.fi/download/noname/%7BEAA3550F-CB3C-4359-A05C-975152698BDF%7D/141803
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
Rannikkovesien pehmeiden pohjien eläinyhteisön seurantaan liittyviä menetelmäohjeistuksia:
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
SFS 5076:1989. Water quality. Sampling of the bottom fauna on soft bottoms with an Ekman grab. Vesitutkimukset. Pohjaeläinnäytteenotto Ekman-noutimella pehmeiltä pohjilta.
SFS-EN ISO 10870:2012 Water quality. Guidelines for the selection of sampling methods and devices for benthic macroinvertebrates in fresh waters (ISO 10870:2012)
SFS 5077:1989. Water quality. Handnet sampling of the bottom fauna in running waters. Vesitutkimukset. Pohjaeläinnäytteenotto käsihaavilla virtaavissa vesissä.
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf Lax H-G, Perus J 2008.
Pehmeiden pohjien pohjaeläinten ja sedimentin näytteenotto rannikkovesien VPD-seurannassa. Teoksessa Vuori et al. (toim.) Vesienhoitoalueiden biologisten seurantojen järjestäminen ja määritysten hankinta. Suomen ympäristökeskuksen raportteja 35, liite 4
Nygård H, 2018. Pohjaeläinnäytteenotto rannikkovesialueilla. https://www.ymparisto.fi/download/noname/%7BEAA3550F-CB3C-4359-A05C-975152698BDF%7D/141803
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
Rannikkovesien pehmeiden pohjien eläinyhteisön seurantaan liittyviä menetelmäohjeistuksia:
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
SFS 5076:1989. Water quality. Sampling of the bottom fauna on soft bottoms with an Ekman grab. Vesitutkimukset. Pohjaeläinnäytteenotto Ekman-noutimella pehmeiltä pohjilta.
SFS-EN ISO 10870:2012 Water quality. Guidelines for the selection of sampling methods and devices for benthic macroinvertebrates in fresh waters (ISO 10870:2012)
SFS 5077:1989. Water quality. Handnet sampling of the bottom fauna in running waters. Vesitutkimukset. Pohjaeläinnäytteenotto käsihaavilla virtaavissa vesissä.
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf Lax H-G, Perus J 2008.
Pehmeiden pohjien pohjaeläinten ja sedimentin näytteenotto rannikkovesien VPD-seurannassa. Teoksessa Vuori et al. (toim.) Vesienhoitoalueiden biologisten seurantojen järjestäminen ja määritysten hankinta. Suomen ympäristökeskuksen raportteja 35, liite 4
Nygård H, 2018. Pohjaeläinnäytteenotto rannikkovesialueilla. https://www.ymparisto.fi/download/noname/%7BEAA3550F-CB3C-4359-A05C-975152698BDF%7D/141803
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
Rannikkovesien pehmeiden pohjien eläinyhteisön seurantaan liittyviä menetelmäohjeistuksia:
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
SFS 5076:1989. Water quality. Sampling of the bottom fauna on soft bottoms with an Ekman grab. Vesitutkimukset. Pohjaeläinnäytteenotto Ekman-noutimella pehmeiltä pohjilta.
SFS-EN ISO 10870:2012 Water quality. Guidelines for the selection of sampling methods and devices for benthic macroinvertebrates in fresh waters (ISO 10870:2012)
SFS 5077:1989. Water quality. Handnet sampling of the bottom fauna in running waters. Vesitutkimukset. Pohjaeläinnäytteenotto käsihaavilla virtaavissa vesissä.
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf Lax H-G, Perus J 2008.
Pehmeiden pohjien pohjaeläinten ja sedimentin näytteenotto rannikkovesien VPD-seurannassa. Teoksessa Vuori et al. (toim.) Vesienhoitoalueiden biologisten seurantojen järjestäminen ja määritysten hankinta. Suomen ympäristökeskuksen raportteja 35, liite 4
Nygård H, 2018. Pohjaeläinnäytteenotto rannikkovesialueilla. https://www.ymparisto.fi/download/noname/%7BEAA3550F-CB3C-4359-A05C-975152698BDF%7D/141803
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
Rannikkovesien pehmeiden pohjien eläinyhteisön seurantaan liittyviä menetelmäohjeistuksia:
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
SFS 5076:1989. Water quality. Sampling of the bottom fauna on soft bottoms with an Ekman grab. Vesitutkimukset. Pohjaeläinnäytteenotto Ekman-noutimella pehmeiltä pohjilta.
SFS-EN ISO 10870:2012 Water quality. Guidelines for the selection of sampling methods and devices for benthic macroinvertebrates in fresh waters (ISO 10870:2012)
SFS 5077:1989. Water quality. Handnet sampling of the bottom fauna in running waters. Vesitutkimukset. Pohjaeläinnäytteenotto käsihaavilla virtaavissa vesissä.
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf Lax H-G, Perus J 2008.
Pehmeiden pohjien pohjaeläinten ja sedimentin näytteenotto rannikkovesien VPD-seurannassa. Teoksessa Vuori et al. (toim.) Vesienhoitoalueiden biologisten seurantojen järjestäminen ja määritysten hankinta. Suomen ympäristökeskuksen raportteja 35, liite 4
Nygård H, 2018. Pohjaeläinnäytteenotto rannikkovesialueilla. https://www.ymparisto.fi/download/noname/%7BEAA3550F-CB3C-4359-A05C-975152698BDF%7D/141803
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
Rannikkovesien pehmeiden pohjien eläinyhteisön seurantaan liittyviä menetelmäohjeistuksia:
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
SFS 5076:1989. Water quality. Sampling of the bottom fauna on soft bottoms with an Ekman grab. Vesitutkimukset. Pohjaeläinnäytteenotto Ekman-noutimella pehmeiltä pohjilta.
SFS-EN ISO 10870:2012 Water quality. Guidelines for the selection of sampling methods and devices for benthic macroinvertebrates in fresh waters (ISO 10870:2012)
SFS 5077:1989. Water quality. Handnet sampling of the bottom fauna in running waters. Vesitutkimukset. Pohjaeläinnäytteenotto käsihaavilla virtaavissa vesissä.
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf Lax H-G, Perus J 2008.
Pehmeiden pohjien pohjaeläinten ja sedimentin näytteenotto rannikkovesien VPD-seurannassa. Teoksessa Vuori et al. (toim.) Vesienhoitoalueiden biologisten seurantojen järjestäminen ja määritysten hankinta. Suomen ympäristökeskuksen raportteja 35, liite 4
Nygård H, 2018. Pohjaeläinnäytteenotto rannikkovesialueilla. https://www.ymparisto.fi/download/noname/%7BEAA3550F-CB3C-4359-A05C-975152698BDF%7D/141803
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
Rannikkovesien pehmeiden pohjien eläinyhteisön seurantaan liittyviä menetelmäohjeistuksia:
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
SFS 5076:1989. Water quality. Sampling of the bottom fauna on soft bottoms with an Ekman grab. Vesitutkimukset. Pohjaeläinnäytteenotto Ekman-noutimella pehmeiltä pohjilta.
SFS-EN ISO 10870:2012 Water quality. Guidelines for the selection of sampling methods and devices for benthic macroinvertebrates in fresh waters (ISO 10870:2012)
SFS 5077:1989. Water quality. Handnet sampling of the bottom fauna in running waters. Vesitutkimukset. Pohjaeläinnäytteenotto käsihaavilla virtaavissa vesissä.
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf Lax H-G, Perus J 2008.
Pehmeiden pohjien pohjaeläinten ja sedimentin näytteenotto rannikkovesien VPD-seurannassa. Teoksessa Vuori et al. (toim.) Vesienhoitoalueiden biologisten seurantojen järjestäminen ja määritysten hankinta. Suomen ympäristökeskuksen raportteja 35, liite 4
Nygård H, 2018. Pohjaeläinnäytteenotto rannikkovesialueilla. https://www.ymparisto.fi/download/noname/%7BEAA3550F-CB3C-4359-A05C-975152698BDF%7D/141803
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
Rannikkovesien pehmeiden pohjien eläinyhteisön seurantaan liittyviä menetelmäohjeistuksia:
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
SFS 5076:1989. Water quality. Sampling of the bottom fauna on soft bottoms with an Ekman grab. Vesitutkimukset. Pohjaeläinnäytteenotto Ekman-noutimella pehmeiltä pohjilta.
SFS-EN ISO 10870:2012 Water quality. Guidelines for the selection of sampling methods and devices for benthic macroinvertebrates in fresh waters (ISO 10870:2012)
SFS 5077:1989. Water quality. Handnet sampling of the bottom fauna in running waters. Vesitutkimukset. Pohjaeläinnäytteenotto käsihaavilla virtaavissa vesissä.
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf Lax H-G, Perus J 2008.
Pehmeiden pohjien pohjaeläinten ja sedimentin näytteenotto rannikkovesien VPD-seurannassa. Teoksessa Vuori et al. (toim.) Vesienhoitoalueiden biologisten seurantojen järjestäminen ja määritysten hankinta. Suomen ympäristökeskuksen raportteja 35, liite 4
Nygård H, 2018. Pohjaeläinnäytteenotto rannikkovesialueilla. https://www.ymparisto.fi/download/noname/%7BEAA3550F-CB3C-4359-A05C-975152698BDF%7D/141803
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
Rannikkovesien pehmeiden pohjien eläinyhteisön seurantaan liittyviä menetelmäohjeistuksia:
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
SFS 5076:1989. Water quality. Sampling of the bottom fauna on soft bottoms with an Ekman grab. Vesitutkimukset. Pohjaeläinnäytteenotto Ekman-noutimella pehmeiltä pohjilta.
SFS-EN ISO 10870:2012 Water quality. Guidelines for the selection of sampling methods and devices for benthic macroinvertebrates in fresh waters (ISO 10870:2012)
SFS 5077:1989. Water quality. Handnet sampling of the bottom fauna in running waters. Vesitutkimukset. Pohjaeläinnäytteenotto käsihaavilla virtaavissa vesissä.
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf Lax H-G, Perus J 2008.
Pehmeiden pohjien pohjaeläinten ja sedimentin näytteenotto rannikkovesien VPD-seurannassa. Teoksessa Vuori et al. (toim.) Vesienhoitoalueiden biologisten seurantojen järjestäminen ja määritysten hankinta. Suomen ympäristökeskuksen raportteja 35, liite 4
Nygård H, 2018. Pohjaeläinnäytteenotto rannikkovesialueilla. https://www.ymparisto.fi/download/noname/%7BEAA3550F-CB3C-4359-A05C-975152698BDF%7D/141803
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
Rannikkovesien pehmeiden pohjien eläinyhteisön seurantaan liittyviä menetelmäohjeistuksia:
SFS-EN ISO 16665:2005. Water quality. Guidelines for quantitative sampling and sample processing of marine soft-bottom macrofauna (ISO 16665:2003)
SFS 5076:1989. Water quality. Sampling of the bottom fauna on soft bottoms with an Ekman grab. Vesitutkimukset. Pohjaeläinnäytteenotto Ekman-noutimella pehmeiltä pohjilta.
SFS-EN ISO 10870:2012 Water quality. Guidelines for the selection of sampling methods and devices for benthic macroinvertebrates in fresh waters (ISO 10870:2012)
SFS 5077:1989. Water quality. Handnet sampling of the bottom fauna in running waters. Vesitutkimukset. Pohjaeläinnäytteenotto käsihaavilla virtaavissa vesissä.
HELCOM Combine manual. Annex C-8 Soft bottom macrozoobenthos http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC8.pdf Lax H-G, Perus J 2008.
Pehmeiden pohjien pohjaeläinten ja sedimentin näytteenotto rannikkovesien VPD-seurannassa. Teoksessa Vuori et al. (toim.) Vesienhoitoalueiden biologisten seurantojen järjestäminen ja määritysten hankinta. Suomen ympäristökeskuksen raportteja 35, liite 4
Nygård H, 2018. Pohjaeläinnäytteenotto rannikkovesialueilla. https://www.ymparisto.fi/download/noname/%7BEAA3550F-CB3C-4359-A05C-975152698BDF%7D/141803
Pohjaeläinten lajiston, lukumäärän ja biomassan määritys. SYKE/MK Sisäinen menetelmä TA201, modifioitu HELCOM-ohjeistuksesta. |
Holgersson E (2013) Kartering av makrofyter, framtagandet av en klassificeringsmetod för att kunna beräkna ekologisk status för Ålands skärgård och skapandet av ett miljöövervakningsprogram. Rapporter från Husö biologiska station, nr 75.
Ruuskanen A, 2014. Rannikkovesien vesipuitedirektiivin mukainen makrofyyttiseuranta. https://www.ymparisto.fi/download/noname/%7B688ED3AE-C8A0-46E6-9919-74273AB55AA4%7D/141802
Saarinen A (2015) Beräkning av ekologisk status för Ålands ytvattenförekomster utgående från kartering av makrofyter: ett förslag till övervakningsprogram och harmonisering av metoder mellan Åland och Finland. Rapporter från Husö biologiska station, nr 75.
SFS-EN ISO 19493:2007. Water quality. Guidance on marine biological surveys of hard-substrate communities (ISO 19493:2007)
SFS-EN 16260:2012 Water quality – Visual seabed surveys ROV using remotely operated and/or towed observation gear for collection of environmental data
VELMU-menetelmäohjeistus - https://www.ymparisto.fi/en-us/VELMU
HELCOM Combine manual. Annex C-9 Guidelines for monitoring of phytobenthic plant and animal communities in the Baltic Sea http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC9.pdf |
Holgersson E (2013) Kartering av makrofyter, framtagandet av en klassificeringsmetod för att kunna beräkna ekologisk status för Ålands skärgård och skapandet av ett miljöövervakningsprogram. Rapporter från Husö biologiska station, nr 75.
Ruuskanen A, 2014. Rannikkovesien vesipuitedirektiivin mukainen makrofyyttiseuranta. https://www.ymparisto.fi/download/noname/%7B688ED3AE-C8A0-46E6-9919-74273AB55AA4%7D/141802
Saarinen A (2015) Beräkning av ekologisk status för Ålands ytvattenförekomster utgående från kartering av makrofyter: ett förslag till övervakningsprogram och harmonisering av metoder mellan Åland och Finland. Rapporter från Husö biologiska station, nr 75.
SFS-EN ISO 19493:2007. Water quality. Guidance on marine biological surveys of hard-substrate communities (ISO 19493:2007)
SFS-EN 16260:2012 Water quality – Visual seabed surveys ROV using remotely operated and/or towed observation gear for collection of environmental data
VELMU-menetelmäohjeistus - https://www.ymparisto.fi/en-us/VELMU
HELCOM Combine manual. Annex C-9 Guidelines for monitoring of phytobenthic plant and animal communities in the Baltic Sea http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC9.pdf |
Holgersson E (2013) Kartering av makrofyter, framtagandet av en klassificeringsmetod för att kunna beräkna ekologisk status för Ålands skärgård och skapandet av ett miljöövervakningsprogram. Rapporter från Husö biologiska station, nr 75.
Ruuskanen A, 2014. Rannikkovesien vesipuitedirektiivin mukainen makrofyyttiseuranta. https://www.ymparisto.fi/download/noname/%7B688ED3AE-C8A0-46E6-9919-74273AB55AA4%7D/141802
Saarinen A (2015) Beräkning av ekologisk status för Ålands ytvattenförekomster utgående från kartering av makrofyter: ett förslag till övervakningsprogram och harmonisering av metoder mellan Åland och Finland. Rapporter från Husö biologiska station, nr 75.
SFS-EN ISO 19493:2007. Water quality. Guidance on marine biological surveys of hard-substrate communities (ISO 19493:2007)
SFS-EN 16260:2012 Water quality – Visual seabed surveys ROV using remotely operated and/or towed observation gear for collection of environmental data
VELMU-menetelmäohjeistus - https://www.ymparisto.fi/en-us/VELMU
HELCOM Combine manual. Annex C-9 Guidelines for monitoring of phytobenthic plant and animal communities in the Baltic Sea http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC9.pdf |
Holgersson E (2013) Kartering av makrofyter, framtagandet av en klassificeringsmetod för att kunna beräkna ekologisk status för Ålands skärgård och skapandet av ett miljöövervakningsprogram. Rapporter från Husö biologiska station, nr 75.
Ruuskanen A, 2014. Rannikkovesien vesipuitedirektiivin mukainen makrofyyttiseuranta. https://www.ymparisto.fi/download/noname/%7B688ED3AE-C8A0-46E6-9919-74273AB55AA4%7D/141802
Saarinen A (2015) Beräkning av ekologisk status för Ålands ytvattenförekomster utgående från kartering av makrofyter: ett förslag till övervakningsprogram och harmonisering av metoder mellan Åland och Finland. Rapporter från Husö biologiska station, nr 75.
SFS-EN ISO 19493:2007. Water quality. Guidance on marine biological surveys of hard-substrate communities (ISO 19493:2007)
SFS-EN 16260:2012 Water quality – Visual seabed surveys ROV using remotely operated and/or towed observation gear for collection of environmental data
VELMU-menetelmäohjeistus - https://www.ymparisto.fi/en-us/VELMU
HELCOM Combine manual. Annex C-9 Guidelines for monitoring of phytobenthic plant and animal communities in the Baltic Sea http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC9.pdf |
Holgersson E (2013) Kartering av makrofyter, framtagandet av en klassificeringsmetod för att kunna beräkna ekologisk status för Ålands skärgård och skapandet av ett miljöövervakningsprogram. Rapporter från Husö biologiska station, nr 75.
Ruuskanen A, 2014. Rannikkovesien vesipuitedirektiivin mukainen makrofyyttiseuranta. https://www.ymparisto.fi/download/noname/%7B688ED3AE-C8A0-46E6-9919-74273AB55AA4%7D/141802
Saarinen A (2015) Beräkning av ekologisk status för Ålands ytvattenförekomster utgående från kartering av makrofyter: ett förslag till övervakningsprogram och harmonisering av metoder mellan Åland och Finland. Rapporter från Husö biologiska station, nr 75.
SFS-EN ISO 19493:2007. Water quality. Guidance on marine biological surveys of hard-substrate communities (ISO 19493:2007)
SFS-EN 16260:2012 Water quality – Visual seabed surveys ROV using remotely operated and/or towed observation gear for collection of environmental data
VELMU-menetelmäohjeistus - https://www.ymparisto.fi/en-us/VELMU
HELCOM Combine manual. Annex C-9 Guidelines for monitoring of phytobenthic plant and animal communities in the Baltic Sea http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC9.pdf |
Holgersson E (2013) Kartering av makrofyter, framtagandet av en klassificeringsmetod för att kunna beräkna ekologisk status för Ålands skärgård och skapandet av ett miljöövervakningsprogram. Rapporter från Husö biologiska station, nr 75.
Ruuskanen A, 2014. Rannikkovesien vesipuitedirektiivin mukainen makrofyyttiseuranta. https://www.ymparisto.fi/download/noname/%7B688ED3AE-C8A0-46E6-9919-74273AB55AA4%7D/141802
Saarinen A (2015) Beräkning av ekologisk status för Ålands ytvattenförekomster utgående från kartering av makrofyter: ett förslag till övervakningsprogram och harmonisering av metoder mellan Åland och Finland. Rapporter från Husö biologiska station, nr 75.
SFS-EN ISO 19493:2007. Water quality. Guidance on marine biological surveys of hard-substrate communities (ISO 19493:2007)
SFS-EN 16260:2012 Water quality – Visual seabed surveys ROV using remotely operated and/or towed observation gear for collection of environmental data
VELMU-menetelmäohjeistus - https://www.ymparisto.fi/en-us/VELMU
HELCOM Combine manual. Annex C-9 Guidelines for monitoring of phytobenthic plant and animal communities in the Baltic Sea http://www.helcom.fi/Documents/Action%20areas/Monitoring%20and%20assessment/Manuals%20and%20Guidelines/Manual%20for%20Marine%20Monitoring%20in%20the%20COMBINE%20Programme%20of%20HELCOM_PartC_AnnexC9.pdf |
VELMU - https://www.environment.fi/en-US/VELMU
Åbo Akademi - http://urn.fi/URN:ISBN:978-952-12-3309-8 |
VELMU - https://www.environment.fi/en-US/VELMU
Åbo Akademi - http://urn.fi/URN:ISBN:978-952-12-3309-8 |
VELMU - https://www.environment.fi/en-US/VELMU
Åbo Akademi - http://urn.fi/URN:ISBN:978-952-12-3309-8 |
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 |
Härkönen, T and S. G. Lunneryd 1992. Estimating abundance of ringed seals in the Bothnian Bay. Ambio 21:497-510.
Härkönen, T., O. Stenman, M. Jüssi, I. Jüssi, R. Sagitov and M. Verevkin 1998. Population size and distribution of the Baltic ringed seal (Phoca hispida botnica). In: Ringed Seals (Phoca hispida) in the North Atlantic. Edited by C.Lydersen and M.P. Heide-Jørgensen. NAMMCO Scientific Publications, Vol. 1, 167–180. |
Härkönen, T and S. G. Lunneryd 1992. Estimating abundance of ringed seals in the Bothnian Bay. Ambio 21:497-510.
Härkönen, T., O. Stenman, M. Jüssi, I. Jüssi, R. Sagitov and M. Verevkin 1998. Population size and distribution of the Baltic ringed seal (Phoca hispida botnica). In: Ringed Seals (Phoca hispida) in the North Atlantic. Edited by C.Lydersen and M.P. Heide-Jørgensen. NAMMCO Scientific Publications, Vol. 1, 167–180. |
Boyd, I. L. 1984. Development and regression of the corpus luteum in grey seal (Halichoerus grypus) ovaries and its use in determining fertility rates. – Canadian Journal of Zoology 62: 1095 –1100.
Boyd, I. L., Lockyer, C. & Marsh, H. D. 1999. Reproduction in marine mammals. – In: Reynolds,
J. E. & Rommel, S. A. (eds.), Biology of marine mammals: 218 –286. Smithsonian Institution Press, Washington.
HELCOM, 2018a. Reproductive status of marine mammals. HELCOM core indicator report. Online. http://www.helcom.fi/baltic-sea-trends/indicators/reproductive-status-of-seals/
HELCOM, 2018b. Nutritional status of seals. HELCOM Core Indicator Report. Online. http://www.helcom.fi/Core%20Indicators/Nutritional%20status%20of%20seals%20HELCOM%20core%20indicator%202018.pdf
Kauhala, K., Ahola, M. P. & Kunnasranta, M. 2012. Demographic structure and mortality rate of a Baltic grey seal population at different stages of population change, judged on the basis of the hunting bag in Finland. – Annales Zoologici Fennici 49: 287– 305.
Kauhala, K. & Kunnasranta, M. 2012. Hallisaaliin määrä ja rakenne Suomen merialueilla. – Suomen Riista 58: 7–15.
Kauhala, K., Kunnasranta, M. & Valtonen, M. 2011. Hallien ravinto Suomen merialueilla 2001–2007
– alustava selvitys. – Suomen Riista 57: 73 – 83.
Kauhala, K., Ahola, M. P. & Kunnasranta, M. 2014: Decline in the pregnancy rate of Baltic grey seal females during the 2000s. – Annales Zoologici Fennici 51: 313–324.
Kauhala, K., Bäcklin, B-M., Harding, K. & Raitaniemi, J. 2017: The effect of prey quality and ice conditions on the nutritional status of Baltic gray seals of different age groups. – Mammal Research 62: 351‒362.
Kauhala, K., Korpinen, S., Lehtiniemi, M. & Raitaniemi, J. 2019: Reproductive rate of a top predator, the grey seal, as an indicator of the changes in the Baltic food web. – Ecological Indicators 102: 693–703.
Kauhala, K. & Kurkilahti, M. 2019: Delayed effects of pup environment on adult size and reproductive rate of Baltic grey sealsMammal Research https://doi.org/10.1007/s13364-019-00454-1 |
Boyd, I. L. 1984. Development and regression of the corpus luteum in grey seal (Halichoerus grypus) ovaries and its use in determining fertility rates. – Canadian Journal of Zoology 62: 1095 –1100.
Boyd, I. L., Lockyer, C. & Marsh, H. D. 1999. Reproduction in marine mammals. – In: Reynolds,
J. E. & Rommel, S. A. (eds.), Biology of marine mammals: 218 –286. Smithsonian Institution Press, Washington.
HELCOM, 2018a. Reproductive status of marine mammals. HELCOM core indicator report. Online. http://www.helcom.fi/baltic-sea-trends/indicators/reproductive-status-of-seals/
HELCOM, 2018b. Nutritional status of seals. HELCOM Core Indicator Report. Online. http://www.helcom.fi/Core%20Indicators/Nutritional%20status%20of%20seals%20HELCOM%20core%20indicator%202018.pdf
Kauhala, K., Ahola, M. P. & Kunnasranta, M. 2012. Demographic structure and mortality rate of a Baltic grey seal population at different stages of population change, judged on the basis of the hunting bag in Finland. – Annales Zoologici Fennici 49: 287– 305.
Kauhala, K. & Kunnasranta, M. 2012. Hallisaaliin määrä ja rakenne Suomen merialueilla. – Suomen Riista 58: 7–15.
Kauhala, K., Kunnasranta, M. & Valtonen, M. 2011. Hallien ravinto Suomen merialueilla 2001–2007
– alustava selvitys. – Suomen Riista 57: 73 – 83.
Kauhala, K., Ahola, M. P. & Kunnasranta, M. 2014: Decline in the pregnancy rate of Baltic grey seal females during the 2000s. – Annales Zoologici Fennici 51: 313–324.
Kauhala, K., Bäcklin, B-M., Harding, K. & Raitaniemi, J. 2017: The effect of prey quality and ice conditions on the nutritional status of Baltic gray seals of different age groups. – Mammal Research 62: 351‒362.
Kauhala, K., Korpinen, S., Lehtiniemi, M. & Raitaniemi, J. 2019: Reproductive rate of a top predator, the grey seal, as an indicator of the changes in the Baltic food web. – Ecological Indicators 102: 693–703.
Kauhala, K. & Kurkilahti, M. 2019: Delayed effects of pup environment on adult size and reproductive rate of Baltic grey sealsMammal Research https://doi.org/10.1007/s13364-019-00454-1 |
Boyd, I. L. 1984. Development and regression of the corpus luteum in grey seal (Halichoerus grypus) ovaries and its use in determining fertility rates. – Canadian Journal of Zoology 62: 1095 –1100.
Boyd, I. L., Lockyer, C. & Marsh, H. D. 1999. Reproduction in marine mammals. – In: Reynolds,
J. E. & Rommel, S. A. (eds.), Biology of marine mammals: 218 –286. Smithsonian Institution Press, Washington.
HELCOM, 2018a. Reproductive status of marine mammals. HELCOM core indicator report. Online. http://www.helcom.fi/baltic-sea-trends/indicators/reproductive-status-of-seals/
HELCOM, 2018b. Nutritional status of seals. HELCOM Core Indicator Report. Online. http://www.helcom.fi/Core%20Indicators/Nutritional%20status%20of%20seals%20HELCOM%20core%20indicator%202018.pdf
Kauhala, K., Ahola, M. P. & Kunnasranta, M. 2012. Demographic structure and mortality rate of a Baltic grey seal population at different stages of population change, judged on the basis of the hunting bag in Finland. – Annales Zoologici Fennici 49: 287– 305.
Kauhala, K. & Kunnasranta, M. 2012. Hallisaaliin määrä ja rakenne Suomen merialueilla. – Suomen Riista 58: 7–15.
Kauhala, K., Kunnasranta, M. & Valtonen, M. 2011. Hallien ravinto Suomen merialueilla 2001–2007
– alustava selvitys. – Suomen Riista 57: 73 – 83.
Kauhala, K., Ahola, M. P. & Kunnasranta, M. 2014: Decline in the pregnancy rate of Baltic grey seal females during the 2000s. – Annales Zoologici Fennici 51: 313–324.
Kauhala, K., Bäcklin, B-M., Harding, K. & Raitaniemi, J. 2017: The effect of prey quality and ice conditions on the nutritional status of Baltic gray seals of different age groups. – Mammal Research 62: 351‒362.
Kauhala, K., Korpinen, S., Lehtiniemi, M. & Raitaniemi, J. 2019: Reproductive rate of a top predator, the grey seal, as an indicator of the changes in the Baltic food web. – Ecological Indicators 102: 693–703.
Kauhala, K. & Kurkilahti, M. 2019: Delayed effects of pup environment on adult size and reproductive rate of Baltic grey sealsMammal Research https://doi.org/10.1007/s13364-019-00454-1 |
Boyd, I. L. 1984. Development and regression of the corpus luteum in grey seal (Halichoerus grypus) ovaries and its use in determining fertility rates. – Canadian Journal of Zoology 62: 1095 –1100.
Boyd, I. L., Lockyer, C. & Marsh, H. D. 1999. Reproduction in marine mammals. – In: Reynolds,
J. E. & Rommel, S. A. (eds.), Biology of marine mammals: 218 –286. Smithsonian Institution Press, Washington.
HELCOM, 2018a. Reproductive status of marine mammals. HELCOM core indicator report. Online. http://www.helcom.fi/baltic-sea-trends/indicators/reproductive-status-of-seals/
HELCOM, 2018b. Nutritional status of seals. HELCOM Core Indicator Report. Online. http://www.helcom.fi/Core%20Indicators/Nutritional%20status%20of%20seals%20HELCOM%20core%20indicator%202018.pdf
Kauhala, K., Ahola, M. P. & Kunnasranta, M. 2012. Demographic structure and mortality rate of a Baltic grey seal population at different stages of population change, judged on the basis of the hunting bag in Finland. – Annales Zoologici Fennici 49: 287– 305.
Kauhala, K. & Kunnasranta, M. 2012. Hallisaaliin määrä ja rakenne Suomen merialueilla. – Suomen Riista 58: 7–15.
Kauhala, K., Kunnasranta, M. & Valtonen, M. 2011. Hallien ravinto Suomen merialueilla 2001–2007
– alustava selvitys. – Suomen Riista 57: 73 – 83.
Kauhala, K., Ahola, M. P. & Kunnasranta, M. 2014: Decline in the pregnancy rate of Baltic grey seal females during the 2000s. – Annales Zoologici Fennici 51: 313–324.
Kauhala, K., Bäcklin, B-M., Harding, K. & Raitaniemi, J. 2017: The effect of prey quality and ice conditions on the nutritional status of Baltic gray seals of different age groups. – Mammal Research 62: 351‒362.
Kauhala, K., Korpinen, S., Lehtiniemi, M. & Raitaniemi, J. 2019: Reproductive rate of a top predator, the grey seal, as an indicator of the changes in the Baltic food web. – Ecological Indicators 102: 693–703.
Kauhala, K. & Kurkilahti, M. 2019: Delayed effects of pup environment on adult size and reproductive rate of Baltic grey sealsMammal Research https://doi.org/10.1007/s13364-019-00454-1 |
HELCOM Combine - https://helcom.fi/media/publications/Guidelines-for-monitoring-of-mesozooplankton.pdf |
HELCOM Combine - https://helcom.fi/media/publications/Guidelines-for-monitoring-of-mesozooplankton.pdf |
HELCOM Combine - https://helcom.fi/media/publications/Guidelines-for-monitoring-of-mesozooplankton.pdf |
HELCOM Combine - https://helcom.fi/media/publications/Guidelines-for-monitoring-of-mesozooplankton.pdf |
HELCOM Combine - https://helcom.fi/media/publications/Guidelines-for-monitoring-of-mesozooplankton.pdf |
HELCOM Combine - https://helcom.fi/media/publications/Guidelines-for-monitoring-of-mesozooplankton.pdf |
Aroviita, J., Mitikka, S., Vienonen S. (toim.) 2019: Pintavesien tilan luokittelu ja arviointiperusteet vesienhoidon kolmannella kaudella. Suomen ympäristökeskuksen raportteja 37 / 2019.
HELCOM 2017: Monitoring of phytoplankton species composition, abundance and biomass. |
Aroviita, J., Mitikka, S., Vienonen S. (toim.) 2019: Pintavesien tilan luokittelu ja arviointiperusteet vesienhoidon kolmannella kaudella. Suomen ympäristökeskuksen raportteja 37 / 2019.
HELCOM 2017: Monitoring of phytoplankton species composition, abundance and biomass. |
Aroviita, J., Mitikka, S., Vienonen S. (toim.) 2019: Pintavesien tilan luokittelu ja arviointiperusteet vesienhoidon kolmannella kaudella. Suomen ympäristökeskuksen raportteja 37 / 2019.
HELCOM 2017: Monitoring of phytoplankton species composition, abundance and biomass. |
Aroviita, J., Mitikka, S., Vienonen S. (toim.) 2019: Pintavesien tilan luokittelu ja arviointiperusteet vesienhoidon kolmannella kaudella. Suomen ympäristökeskuksen raportteja 37 / 2019.
HELCOM 2017: Monitoring of phytoplankton species composition, abundance and biomass. |
Aroviita, J., Mitikka, S., Vienonen S. (toim.) 2019: Pintavesien tilan luokittelu ja arviointiperusteet vesienhoidon kolmannella kaudella. Suomen ympäristökeskuksen raportteja 37 / 2019.
HELCOM 2017: Monitoring of phytoplankton species composition, abundance and biomass. |
Aroviita, J., Mitikka, S., Vienonen S. (toim.) 2019: Pintavesien tilan luokittelu ja arviointiperusteet vesienhoidon kolmannella kaudella. Suomen ympäristökeskuksen raportteja 37 / 2019.
HELCOM 2017: Monitoring of phytoplankton species composition, abundance and biomass. |
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 |