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Radioactivity in the Baltic Sea

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Radioactivity in the Baltic Sea

Finland has been a forerunner in the monitoring of radioactivity in the Baltic Sea. Radioactivity surveys were initiated as early as the end of the 1950s by STUK’s predecessor Institute of Radiation Physics in co-operation with the Finnish Institute of Marine Research.

An impulse for these activities was given by the above-ground nuclear weapon tests carried out in Novaya Zemlya in the 1950s and 1960s. Gradually the surveillance expanded into co-operation between all the Baltic Sea countries. The fallout from nuclear weapon tests was distributed relatively evenly throughout the Baltic Sea catchment basin, containing mainly cesium-137 and strontium-90.

In 1986, the radioactive plume from Chernobyl was carried by winds directly towards the Baltic Sea, causing a fallout that was distributed quite unevenly.  The Baltic Sea received more of the Chernobyl fallout than other seas in the world (e.g.,  the Black Sea, the Mediterranean Sea, the North Sea and the northeast Atlantic). On the basis of the amount of cesium-137 carried in the fallout, the Baltic Sea can be classified as one of the most radioactively contaminated sea regions in the world, together with the Irish Sea.

Other significant sources of radioactivity are the two spent nuclear fuel waste treatment facilities: Sellafield in the UK and La Hague in France. The share of other nuclear facilities in the Baltic Sea catchment basin in the activity of Cs-137 and Sr-90 is less than one per cent.

Cesium-137

A pie chart of the sources of cesium-137 in the Baltic Sea. Most of the sources of cesium-137 in the Baltic Sea, 80%, originate from the fallout caused by the Chernobyl nuclear power plant accident. Other sources of release are nuclear weapons (16%), Sellafield and LaHague nuclear fuel waste treatment facilities (5%) as well as releases from nuclear facilities (<0,1 %).

Strontium-90

A pie chart of the sources of strontium-90 in the Baltic Sea. Most of the sources of strontium-90 in the Baltic Sea, approximately 82%, originate from the fallout caused by nuclear weapon testing in the atmosphere during the 1950s and 1960s. Other sources of release are the Chernobyl nuclear power plant accident (11%), Sellafield and LaHague nuclear fuel waste treatment facilities (6%) as well as releases from nuclear facilities (<0,1 %).

During the more than thirty years that have passed since the accident, cesium has disappeared from the water of the Baltic Sea relatively fast, as it has sunk to the bottom with sedimenting material. While the highest cesium-137 concentrations measured immediately following the accident at some locations in the Gulf of Finland and the Sea of Bothnia were approximately 5,000 becquerels per cubic metre, in 2019 the concentrations had fallen below one two-hundredth (< 25 Bq/m³). The Gulf of Finland has been cleared somewhat faster than the Sea of Bothnia. This is due to different sedimentation rates and more efficient water exchange between the Gulf of Finland and the Baltic Proper.

Graph of cesium-137 activity concentrations in surface water in different parts of the Baltic Sea from 1980 to 2019. In the Bothnian Sea, the Baltic Sea, the Gulf of Bothnia and the Gulf of Finland, the concentrations of cesium-137 in surface water increased in the mid-1980s. This was due to the Chernobyl nuclear power plant accident. Concentrations have been declining gradually and are now almost at tolerance levels. The tolerance level is set at the average level detected before the Chernobyl nuclear power plant accident.

Cesium-137 concentrations in surface water in different parts of the Baltic Sea from 1980 to 2019.

At the moment, most of the cesium-137 present in the Baltic Sea is buried in the bottom sediments. The regional distribution of cesium in the bottom sediment is largely in line with the distribution of the Chernobyl fallout.

The magnitude of cesium-137 activity in bottom sediments in the Baltic Sea area from 2011 to 2015. The highest concentrations have been detected in the eastern parts of the Gulf of Finland and the Bothnian Sea.

Cs-137 concentrations in Baltic Sea sediments from 2011 to 2015.

The cesium-137 concentrations in Baltic Sea fish are less than 15 Bq/kg, clearly lower compared with freshwater fish. Therefore, the radiation dose received by Finns from Baltic Sea fish has remained low, being a few thousandths of a millisievert per year.

Graph of cesium-137 activity concentrations in Baltic herring in different parts of the Baltic Sea from 1984 to 2019. The activity concentrations in Baltic herring is monitored in six sampling areas in Hailuoto, Vaasa, Olkiluoto, Seili, Tvärminne and Loviisa. Due to the Chernobyl nuclear power plant accident, cesium-137 activity concentrations increased approximately fiftyfold compared with the previous years in the mid-1980s. Concentrations have been declining gradually and are now almost at tolerance levels. The tolerance level is set at the average level detected before the Chernobyl nuclear power plant accident.

Cs-137 concentration in Baltic herring in Finnish coastal waters from 1984 to 2019.

STUK is engaged in international monitoring of radioactivity in the Baltic Sea, carried out in accordance with the recommendation of the Helsinki Commission. The results of the monitoring are also available on the website of the Helsinki Commission.

The Surveillance of Environmental Radiation in Finland Annual Report also includes the results of the monitoring of radioactivity in the Baltic Sea. The Annual Reports are available in the electronic publication archive Julkari (Julkari.fi).
Updated 30.10.2020