Development of Ecosystem component maps
Henna Rinne, HELCOM Secretariat henna.rinne@helcom.fi 6.9.2016
Development of Ecosystem component maps Henna Rinne, HELCOM - - PowerPoint PPT Presentation
Development of Ecosystem component maps Henna Rinne, HELCOM Secretariat henna.rinne@helcom.fi 6.9.2016 40 Ecosystem component layers Pelagic habitats (2) Broad-scale seabed habitats (6) Habitat forming species (5) Natura 2000
Henna Rinne, HELCOM Secretariat henna.rinne@helcom.fi 6.9.2016
TAPAS workshop 6.9.2016 2
– Springtime (weeks 12-22) Chl-a concentration used as a proxy. Areas with high phytoplankton production are given higher importance – Data: satellite data (MERIS) for 2011 (or potentially mean of years 2009-2011). No MERIS data available for years 2012-1016. Data provided by the Finnish Environment Institute. For Danish area probably complemented with MODIS data.
– Areas not suffering from hypoxia (O2 concentration > 2mg/l). If possible, areas weighed with O2 concentration (higher concentration, higher importance). – Data: requests to SMHI and to IOW made. Final data source, format and timescale still uncertain.
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‒ Infralittoral mud ‒ Infralittoral sand ‒ Infralittoral hard bottom ‒ Circalittoral mud ‒ Circalittoral sand ‒ Circalittoral hard bottom
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generalizations chosen due to lack of suitable substrate data
presence (1) and absence (0) to the BSII
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– Polygon data received, the methods and the coverage of the marine area vary between countries – Converted to 1 km grid cells, Data as presence (1) and absence (0) to the BSII
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– Cod spawning: Based on Hüssy, K. 2011. Review of western Baltic cod (Gadus morhua) recruitment dynamics. ICES Journal of Marine Science 68(7), 1459-1471. – Cod abundance: Baltic International Trawl Survey (BITS) data from ICES. – Map values normalized in the BSII
years summed) was >0.5 tonnes and the number of years when cod has been caught within the statistical rectangle was >1, the area was considered as cod distribution area. A value corresponding low CPUE values was given to these areas.
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Hüssy 2011
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– Baltic International Acoustic Survey (BIAS) data, average of 2011-2015. Reported as millions of fish/ICES statistical rectangle. Outside BIAS coverage, landings data used. – For herring, the landings data indicated distribution across the Baltic Sea, thus a constant value of 10 (millions of herring/ICES rectangle) was given to all areas outside BIAS data, corresponding to low abundance. – For sprat BIAS surveys cover almost the whole distribution area. Few areas with significant sprat landings but outside BIAS area value of 1 (millions of sprat/ICES rectangle) was given corresponding to low abundance. – The map values are normalized in the BSII
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– Demersal spawning: The distribution area delineated by selecting area with depth < 50m within ICES subdivisions 25-32 (Florin & Höglund 2008, Florin et
Bothnian Bay and Quark, as well as Russian part of Gulf of Finland were excluded from the map, according to HELCOM sub-basin division. Presence (1) absence (0) data to the BSII. – Pelagic spawning: Baltic International Trawl Survey (BITS) data, reported per ICES subdivision, average of 2011-2016, quarter 1. In the subdivisions 25, 26 and 28 also demersal spawners can be included in the CPUE values (Florin et
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– No reliable data for adults across the Baltic Sea (gaps in landings data, coastal fish monitoring data scarce in many areas) – Recruitment areas essential for maintaining fish populations – Modelling studies exist for fish recruitment areas thresholds for environment requirements for fish recruitment
– Depth (Baltic Sea Bathymetry database) – Exposure (Wave Impact Index Isæus 2004) – Salinity (May means for 2011-2014, Copernicus Marine Environment Monitoring Service) – Secchi depth (MERIS data for May 2011, Tartu Observatory) Presence (1) absence (0) maps to the BSII
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Generalized to 1km grid
Generalized to 1km grid
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– Sweden leading the data collation and map production (Related to HELCOM Rec 34/1). – Data call on SPAs and IBAs sent in June, again in August. Deadline 23 September. – Wish for the separation of breeding and wintering areas, if possible. – Migration routes may be difficult.
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– Seals: Count data collated in BALSAM project, reported per HELCOM sub-basin / country (e.g. Swedish Bothnian Bay). Haul-out sites reported as points (coordinates). – Harbour porpoise: Probability for detection maps from SAMBAH project will be available – delivery schedule still uncertain
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Method:
Method:
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Method:
Method:
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