Member State report / Art11 / 2020 / D4 / Finland / Baltic Sea
Report type | Member State report to Commission |
MSFD Article | Art. 11 Monitoring programmes (and Art. 17 updates) |
Report due | 2020-10-15 |
GES Descriptor | D4 Food webs/D1 Ecosystems |
Member State | Finland |
Region/subregion | Baltic Sea |
Reported by | Finnish Environment Institute |
Report date | 2020-10-31 |
Report access |
Descriptor |
D4/D1 |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
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). |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Coverage of GES criteria |
Adequate monitoring was in place in 2014 |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Gaps and plans |
No gaps.
|
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Related targets |
|
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Coverage of targets |
Adequate monitoring was in place in 2014 |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Related measures |
|
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Coverage of measures |
Adequate monitoring was in place in 2014 |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Related monitoring programmes |
|
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Programme code |
BALFI-D01,04,06ben-1 |
BALFI-D01,04,06ben-2 |
BALFI-D01,04,06ben-3 |
BALFI-D01,04,06ben-5 |
BALFI-D01,04,06bir-1 |
BALFI-D01,04,06bir-2 |
BALFI-D01,04,06bir-4 |
BALFI-D01,04,06mam-1 |
BALFI-D01,04,06mam-2 |
BALFI-D01,04,06mam-3 |
BALFI-D01,04,06pel-1 |
BALFI-D01,04,06pel-2 |
BALFI-D03-1 |
BALFI-D03-2 |
BALFI-D05-3 |
BALFI-d01,04,06bir-3 |
BALFI-d01,04,06bir-5 |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Programme name |
Offshore soft bottom macrozoobenthos |
Coastal waters soft bottom fauna |
Coastal hard bottom macroalgae and blue mussel communities |
Soft bottom macrophytes |
Marine breeding birds |
Marine wintering birds |
White tailed eagle breeding success |
Seal adundance |
Seal state of health |
Abundance and distribution of harbour porpoises |
Zooplankton species composition and abundance |
Phytoplankton species composition, abundance and biomass |
Fisheries data collection |
Commercial fisheries catch statistics |
Phytoplankton pigments |
Mass mortalities of breeding sea birds |
Hunting of sea birds and seals |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Update type |
Same programme as in 2014 |
Same programme as in 2014 |
Modified from 2014 |
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 |
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 |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Old programme codes |
|
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
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 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. |
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. |
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 |
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.
|
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 kil...
|
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 |
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.
|
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.
|
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 |
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 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Other policies and conventions |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Regional cooperation - coordinating body |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Regional cooperation - countries involved |
DE,DK,EE,LT,LV,PL,SE |
EE,SE |
DE,DK,EE,LT,LV,PL,SE |
DE,DK,EE,LT,LV,PL,SE |
DE,DK,EE,LT,LV,PL,SE |
SE |
DE,DK,PL,SE |
DE,DK,EE,LT,LV,PL,SE |
DE,DK,EE,LT,LV,PL,SE |
DE,DK,EE,LT,LV,SE |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Regional cooperation - implementation level |
Coordinated data collection |
Agreed data collection methods |
Common monitoring strategy |
Coordinated data collection |
Agreed data collection methods |
Common monitoring strategy |
Coordinated data collection |
Coordinated data collection |
Agreed data collection methods |
Coordinated data collection |
Coordinated data collection |
Agreed data collection methods |
Agreed data collection methods |
Coordinated data collection |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
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. |
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 basi...
|
No monitoring in Bothnian Bay since species monitored do not habitat that area |
Diving transects and bathyscope
|
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. |
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/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. |
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. |
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, ...
|
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Features |
Shelf ecosystems
|
Eutrophication
|
Benthic broad habitats
|
Chemical characteristics
|
Physical and hydrological characteristics
|
Physical and hydrological characteristics
|
Shelf ecosystems
|
Physical and hydrological characteristics
|
Shelf ecosystems
|
Eutrophication
|
Benthic broad habitats
|
Chemical characteristics
|
Physical and hydrological characteristics
|
Newly introduced non-indigenous species
|
Established non-indigenous species
|
Eutrophication
|
Benthic broad habitats
|
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
|
Adverse effects on species or habitats
|
Small toothed cetaceans
|
Pelagic broad habitats
|
Newly introduced non-indigenous species
|
Established non-indigenous species
|
Shelf ecosystems
|
Pelagic broad habitats
|
Newly introduced non-indigenous species
|
Shelf ecosystems
|
Eutrophication
|
Pelagic shelf fish
|
Commercially exploited fish and shellfish
|
Benthic-feeding birds
|
Pelagic-feeding birds
|
Surface-feeding birds
|
Small toothed cetaceans
|
Seals
|
Commercially exploited fish and shellfish
|
Coastal ecosystems
|
Fish and shellfish harvesting (professional, recreational)
|
Shelf ecosystems
|
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 |
D4C1 |
D4C1 |
D4C2 |
D4C2 |
D5C8 |
D6C5 |
D7C2 |
NotRelevan |
NotRelevan |
D2C1 |
D2C2 |
D5C6 |
D5C7 |
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 |
D1C2 |
D3C1 |
D3C2 |
D3C3 |
D1C1 |
D1C1 |
D1C1 |
D1C1 |
D1C1 |
D3C1 |
D3C2 |
D3C3 |
D4C1 |
D4C2 |
NotRelevan |
D4C2 |
D4C4 |
D5C2 |
D5C3 |
D1C3 |
D1C3 |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
||||||||||||
Parameters |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|||
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 |
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 |
Number of spawning individuals; Number of smolts |
Number of spawning individuals; Number of smolts |
Age |
age |
age |
Abundance of Cyprinidae |
Fishing effort (days) |
Biomass |
Mortality |
Mortality |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Spatial scope |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Marine reporting units |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Temporal scope (start date - end date) |
1964-9999 |
1964-9999 |
1993-9999 |
2020-9999 |
1948-9999 |
1975-9999 |
1972-9999 |
1988-9999 |
1998-9999 |
2001-9999 |
1979-9999 |
1979-9999 |
2002-9999 |
1980-9999 |
1979-9999 |
1986-9999 |
1971-9999 |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Monitoring frequency |
Yearly |
Yearly |
Yearly |
3-yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Continually |
Yearly |
Yearly |
Yearly |
Continually |
Continually |
Other |
Continually |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Monitoring type |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Monitoring method |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
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. |
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. |
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 |
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 |
Monitoring - https://stat.luke.fi/en/commercial-marine-fishery |
https://helcom.fi/media/documents/Water-column-habitats-Pigments.pdf |
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. |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
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. |
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
|
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) |
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 ...
|
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.
|
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 |
Quality control incorporated to national monitoring |
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 |
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 |
https://stat.luke.fi/tilasto/4428/laatuseloste/4697
|
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
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. |
Stored in SYKE's POHJE database. Currently also submitted to ICES and used in the HELCOM indicator. |
Database being constructed for the monitoring data. |
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 |
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. |
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
|
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. |
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
|
Mortality data not publicly available
Bird ringing data available online |
Primary data only accessible for researchers
|
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Data access |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Related indicator/name |
|
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Contact |
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 |
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/helcom-at-work/groups/state-and-conservation/eg-mama. |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
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. |
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 |
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., 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 |
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 |
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. |
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 |