Metadata
Technical information
1. Source: Finnish Institute of Marine Research, contact persons Anniina Kiiltomäki and Tapani Stipa.
2. Description of data:
Reference and target -levels:
Table 1. Reference and acceptable deviation levels for the open Baltic sea are specified by Helcom, 2006 (Baltic Sea Environ. Proc. No. 104).
| Basin | Basin | DIN | DIP | Chla | DIN/DIP | DIN/SiO4 | |||
| number | name | Ref. | Ad. | Ref. | Ad. | Ref. | Ad. | Ref. | Ref. |
| 1 | Bothnian Bay | 3,50 | 5,25 | 0,10 | 0,15 | 1,00 | 1,50 | 16 | 1 |
| 2 | Bothnian Sea | 2,00 | 3,00 | 0,20 | 0,30 | 1,00 | 1,50 | 16 | 1 |
| 3 | Gulf of Finland | 2,50 | 3,75 | 0,30 | 0,45 | 1,20 | 1,80 | 16 | 1 |
| 4 | Northern Gotland Basin | 2,00 | 3,00 | 0,25 | 0,38 | 1,00 | 1,50 | 16 | 1 |
| 5 | Gulf of Riga | 4,00 | 6,00 | 0,13 | 0,20 | 1,10 | 1,65 | 16 | |
| 6 | Western Gotland Basin | 2,00 | 3,00 | 0,25 | 0,38 | 1,00 | 1,50 | 16 | |
| 7 | Eastern Gotland Basin | 2,29 | 3,44 | 0,35 | 0,53 | 1,40 | 2,10 | ||
| 7b | Lithuanian open waters | 5,00 | 7,50 | 0,30 | 0,45 | 3,00 | 4,50 | 16 | |
| 7c | South east Gotland Basin | 2,50 | 3,75 | 0,25 | 0,38 | ^^1,4 | 2,10 | ||
| 7d | Gdansk Deep | 4,25 | 6,38 | 0,25 | 0,38 | ^^1,4 | 2,10 | ||
| 8 | Bornholm Basin | 1,70 | 2,55 | 0,34 | 0,51 | 1,40 | 2,10 | ||
| 9 | Arkona Basin | 2,44 | 3,66 | 0,29 | 0,44 | 1,40 | 2,10 | ||
| Reference values and acceptable deviation are from: | |||||||||
| Bold | Ref. values are from Helcom, 2006. Baltic Sea Environ. Proc. No. 104 | ||||||||
| Acceptable deviations are calculated as 150% of reference values | |||||||||
| ^^ | Value from basin beside | ||||||||
Figure 21. The HELCOM open water areas listed in Table 1.
Observations:
Original unit of measure: nutrients, silicate µmol l -1
Original unit of measure: Chl a mg m-3
Original purpose of the data: Phytoplankton monitoring of FIMR, Alga@line project
BalEco™ model:
Operational ecosystem model running at the Finnish Institute of Marine Research. The analysis is based on the +6 hour forecast time series of the model. FIMR HELCOM COMBINE observations have been assimilated into the model, but the model results are independent of the Alg@line time series.
3. Geographical coverage: Alg@line: Gulf of Finland, the Baltic Proper. BalEco: Bothnian Sea, Baltic Proper
Figure 22. The Alg@line sampling locations on the route of M/S Finnpartner between Travemünde- Helsinki and the BalEco™ model transect in the Bothnian Sea. The Alg@line sampling locations are on following regions of the Baltic Sea: 1-2; Arkona Basin, 3-5 Bornholm Basin, 6-12; Eastern Gotland Basin, 13-18; Northern Gotland Basin and 19-24; Gulf of Finland. The vertical analysis location are BY5 and LL12. The locations of the first sight Alg@line-figures are: 3,4=AB; 5,6=BB; 11,12=GB_E; 14,15=GB_N; 18,19=GoF.
4. Temporal coverage:
Alg@line-reference: 1993-2005, Analysis: 2006
Winter period: January to February
(Winter averages of January-February considered to be enough equal to period December-February that results only from January 2006 could be used.)
Summer period: June to September
5. Methodology and frequency of data collection:
Automated flow-through sampling system on merchant ships, sampling depth ca. 5 m, Weekly biweekly monthly sampling during the period January- December.
6. Methodology of data manipulation: None.
Quality information
7. Strength and weakness (at data level):
Strength: Medium temporal and spatial sampling frequency. Weakness: storage time of samples from hours to a couple of days depending on the sampling site. The Alg@line sampling depth is 5m and presents 0-5m watermass.
8. a) Reliability, accuracy, precision, robustness (at data level) of Alg@line:
Measurement uncertainty: Chl a: 0.5 mg m-3 if the concentration < 5.0 mg m-3, 1.0 mg m-3 if the concentration > 5.0 mg m-3.
Measurement uncertainty: Phosphate 20-30%, Nitrate 14-20% and Nitrite 12-45%, Ammonium 20-60%, Silicate15-50%
8. b) Reliability, accuracy, precision, robustness of BalEco™ model:
The accuracy of the forecast model BalEco™, compared against the Alg@line observations in 2006, is illustrated in Figure 17. The statistical indicators mean error (ME), mean absolute error (MAE) and root mean square error (RMSE) were calculated for every Alg@line water sample location along the route of the M/S Finnpartner. The time period was same as in Alg@line measurements. The ecosystem model has currently limitations in the description of nutrient field development in the winter and in anoxic conditions on the process level.
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Figure 23. The ME MAE, RMSE of DIP (left up), DIN (right up), SiO4 (left down) and Chla (right down) on each water sample location; 6h forecast. The legend-box shows the values calculated to the entire area. Click images to enlarge!
9. Further work required (for data level and indicator level):
Comments from HELCOM MONAS for further development of the indicator report are welcome.






