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Forest fires in the Chornobyl area
- The exclusion zone around the Chornobyl (Russian: Chernobyl) nuclear power plant was severely contaminated by the reactor accident in 1986. This has had long-lasting effects.
- If the radioactively contaminated forests in the exclusion zone were to burn, the radionuclides contained in the biomass and in the uppermost organic soil layers would be released into the atmosphere.
- Smaller radioactive particles would then be transported over long distances and would also reach Germany if air currents were unfavourable.
- The activity concentrations in Germany are quite low and harmless from the perspective of radiation protection.
The Chornobyl reactor accident in Ukraine in 1986 released large quantities of radioactive substances into the environment. While highly volatile substances (e.g. radioactive caesium or radioactive iodine) reached high altitudes because of the high temperatures of the burning reactor and dispersed widely with the wind and weather, non-volatile radioactive substances (e.g. strontium and plutonium) were deposited mainly in the immediate vicinity of the Chornobyl (Russian: Chernobyl) nuclear power plant in Ukraine as well as in the neighbouring areas of Belarus. The immediate vicinity of the nuclear power plant in particular was severely contaminated.
To this day, radioactive caesium and strontium and transuranic elements such as plutonium and americium can be found in the immediate vicinity of the Chornobyl nuclear power plant because of their long half-lives. In 1986, an exclusion zone was set up in order to protect the population from the high levels of radiation in the vicinity of the damaged reactor. Around 10% of the total radioactive substances released in the Chernobyl accident have been deposited within the exclusion zone.
Forest fires in the exclusion zone can have radiological consequences
If trees, bushes, grass and the top organic soil layers dry out due to the weather, the risk of forest fires increases.
In the forests of the exclusion zone around Chornobyl, most of the radioactive substances released during the reactor accident in 1986 and subsequently deposited are found in the uppermost organic soil layers and in the biomass (e.g. in trees, shrubs, and grass).
In the event of a forest fire, the radioactive substances deposited there would be released into the atmosphere, rise to different heights with the fire smoke, and be dispersed with the air currents. The amount and activity of radioactive substances that could be released in a forest fire are considerably lower than in the 1986 reactor accident.
If trees, shrubs, grass and, the top organic soil layers were to dry out because of weather conditions, the risk of forest fires would increase. A forest fire could then be triggered by a lightning strike, for example. The risk of forest fires in the exclusion zone is further increased because there is no forest management, and there are thus large quantities of easily combustible deadwood.
Forest fires can release radioactivity into the atmosphere
The amount of radioactivity released into the atmosphere during a forest fire depends on many factors such as
- the size of the burning area
- the type and activity of radionuclides in the above-ground biomass (e.g. in trees, shrubs and grass) and in the upper organic forest soil layers
- the moisture content of the above-ground biomass and the upper organic soil layers
- the fire conditions, especially the fire temperature
- the weather conditions, especially wind and precipitation
Depending on the intensity of the fire and the contamination of the burning surfaces, people in the immediate vicinity of the fires (in or near the smoke plume) may be exposed to increased radiation through the inhalation of radionuclides released from the biomass and soil. Even outside the exclusion zone around Chornobyl, radioactive substances can be detected in the air during large forest fires.
Radiological consequences of forest fires in the Chornobyl exclusion zone
If contaminated forests were to burn, the radionuclides contained in the biomass and in the uppermost organic soil layers would be partly released into the atmosphere. Because of the thermal buoyancy force, the radioactive particles would be spatially distributed and deposited with wind and weather.
- Larger particles would then be quickly deposited in the immediate vicinity.
- Smaller particles can be transported and deposited over long distances by the wind. The proportion in the air would decrease as the transport path increases. In dry weather, relatively few particles would be deposited during transport. However, if it rained, the radioactive particles would be washed out of the atmosphere and deposited with the rain. This would then lead to the (additional) radioactive contamination of the area concerned.
Immediate surroundings (Chornobyl)
Radiological consequences for the immediate surroundings
Protective cover over the damaged Chornobyl reactor (New Safe Confinement)
Source: SvedOliver/Stock.adobe.com
The area surrounding the Chornobyl nuclear power plant is contaminated with varying levels of radioactivity. If radionuclides were to be released during forest fires and deposited in the immediate vicinity, areas that were previously only slightly contaminated would become considerably contaminated (secondary contamination).
Reactor block 4 of the Chornobyl nuclear power plant, which was damaged in 1986, and the "sarcophagus" initially erected above it to protect it from radioactive releases are protected from forest fires by a huge protective shell with a height of about 110 metres, a length of 165 metres, and a span of about 260 metres – the "New Safe Confinement".
However, the immediate vicinity of the destroyed reactor block is highly contaminated. There are also interim storage facilities for radioactive waste and facilities for the treatment and processing of radioactive waste in the vicinity of the nuclear power plant.
If forest fires were to occur in the immediate vicinity of the destroyed Unit 4, this would most likely result in the release of large quantities of radionuclides and would considerably delay further safety measures currently taking place (e.g. the relocation of the more than 20,000 fuel elements from the wet storage facility to a dry interim storage facility, the dismantling of the unstable parts of the old sarcophagus, the salvage of the material containing nuclear fuel, and the safe final disposal of this).
Further surroundings (Germany)
Radiological consequences for the further surroundings (Germany)
In the case of unfavourable air currents, small radioactive particles would also reach Germany – but only in negligible quantities. This is because even in highly contaminated areas, forest fires would release considerably less radioactivity than the 1986 reactor accident. The radionuclides would also be strongly diluted during the long transport to Germany.
The additional radiation to which people in Germany would be exposed through forest fires in the radioactively contaminated environment of Chornobyl would be extremely small – even under unfavourable circumstances (for example, in the case of radioactive caesium (caesium-137), this would be about 10 million times smaller than after the reactor accident in 1986). From the perspective of radiation protection, this would pose no danger to the health of humans or the environment.
The BfS assesses the radiological consequences for Germany
If unusual releases of radionuclides are to be expected or have already occurred (e.g. in the case of forest fires in highly contaminated areas), the BfS first examines the possible radiological effects on Germany. Model calculations by the German Weather Service allow us to predict whether the radioactive particles released from the site of the forest fire would reach Germany at all.
Air dust collector at the BfS monitoring station Schauinsland
If air masses with radioactive particles were to reach Germany, the low activity concentrations in the air could be measured only with the help of extremely sensitive measuring systems (e.g. those used by the BfS trace measuring station on the Schauinsland near Freiburg). The activity concentrations in the air would be so low that other early warning systems (e.g. the ODL measuring network) would be unable to detect them. Trace measuring stations in other European countries also continuously measure the activity concentration of radionuclides in the air and exchange this information with each other. As a member of this scientific network, the BfS also receives all relevant data from the other countries.
The BfS assesses the radiological situation in Germany based on its own measurements, the measurements of other European trace measuring stations, and atmospheric dispersion calculations and informs the Federal Environment Ministry, the media, and the general public.
State of 2023.02.10