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Environmental contamination and other consequences of the Chornobyl reactor accident
- The accident at the Chornobyl (Russian: Chernobyl) nuclear power plant in 1986 released radioactive substances – including iodine, caesium, strontium, and plutonium – into the atmosphere.
- In Central Europe, only caesium-137 is relevant for the radiation to which humans and the environment are still exposed.
- In the immediate vicinity of the Chernobyl nuclear power plant, several other long-lived (i.e. slowly decaying) radionuclides also play a role.
- In Germany, forest products such as some species of mushrooms or wild boar from areas that were more highly contaminated in 1986 can still be problematic.
- From a radiation protection point of view, tourist visits to the immediate vicinity of the Chernobyl nuclear power plant are advised against.
- Wind and weather determined the spatial distribution and deposition of radioactive substances
- The situation in 1986
- The situation today
- What should be kept in mind when visiting Belarus, Ukraine, and especially the immediate vicinity of the Chornobyl nuclear power plant?
- What was the situation before 26 April 1986?
The Chornobyl (Russian: Chernobyl) reactor disaster in Ukraine released large quantities of radioactive substances into the atmosphere over about 10 days in 1986. Among the radionuclides released were
- highly volatile iodine and caesium isotopes such as radioactive iodine (iodine-131) and radioactive caesium (caesium-134 and caesium-137) as well as
- non-volatile strontium isotopes such as strontium-90 and transuranic elements such as plutonium and americium.
Non-volatile radioactive substances such as strontium and plutonium were mainly deposited in the immediate vicinity of the Chornobyl nuclear power plant in Ukraine as well as in the bordering areas of Belarus.
Highly volatile radioactive substances such as iodine and caesium reached heights of over one kilometre as a result of the thermal uplift. This allowed them to spread not only in the immediate vicinity of the reactor but also across the northern hemisphere, especially over Europe. The high temperatures caused by burning graphite in the reactor were responsible for the thermal uplift.
Wind and weather determined the spatial distribution and deposition of radioactive substances
Dispersion of radioactive clouds in the period from 27 April to 6 May 1986 due to the accident at the Chernobyl nuclear power plant
The winds prevailing at the start of the release on 26 April 1986 transported the radionuclides that had escaped from the reactor in an initial radioactive cloud over Poland towards Scandinavia. A second radioactive cloud moved over Slovakia, the Czech Republic, and Austria towards Germany. The third cloud finally reached Romania, Bulgaria, Greece, and Turkey. The release ended after 10 days on 6 May 1986.
The wind directions during the release phase determined the spatial distribution of the radioactive clouds.
Whether and how much rain fell during the passage of the radioactive air masses determined where the radioactive substances contained in the clouds were deposited in the environment as well as in what quantities. The regions where it rained as the radioactive clouds passed were subject to particularly high contamination because the rain washed the radionuclides out of the air. Because rainfall occurred at different intensities, the radioactive contamination in the affected areas varied considerably.
The situation in 1986
The radiological situation in the (immediate) vicinity of the Chornobyl nuclear power plant and in Germany was different in 1986:
Germany (1986)
The radiological situation in Germany in 1986
Soil contamination with caesium-137 in 1986 (Bq/m²). Since then, a little over one half of caesium-137 has decayed. The map well reflects the current situation (2022), when multiplying the contamination levels by 0.44.
At the end of April/beginning of May 1986, the radioactive air masses from the Chornobyl reactor accident arrived in Germany. Because there was heavy local precipitation in Southern Germany at this time, Southern Germany was significantly more polluted than Northern Germany:
- Locally, up to 100,000 becquerels of radioactive caesium-137 per square metre – and sometimes more – were deposited in the Bavarian Forest and south of the Danube.
- In the North German Plain, on the other hand, the activity deposition of this radionuclide rarely exceeded 4,000 becquerels per square metre.
The activity deposits of radioactive caesium-134 were about half of those of caesium-137.
The radioactive substances were also deposited in forests, fields, and meadows. The direct deposition of radioactive substances on pastures and a few crops ready for harvest quickly led to high levels of radioactive iodine-131 in cow's milk and leafy vegetables (e.g. spinach) ready for harvest in Southern Germany..
Radionuclides relevant for Germany in 1986
Because of its short half-life of about 8 days, the radioactive iodine-131 had already largely decayed after only a few weeks. The contamination with radioactive iodine-131 came from an amount of less than 1 gram that had been deposited over what was then the Federal Republic of Germany.
Radioactive caesium (caesium-137 and caesium-134) entered plant-based foodstuffs and feed through the leaves after direct deposition on the aerial parts of the plant. According to the Gesellschaft für Strahlen- und Umweltforschung (GSF; now HMGU, Helmholtz Zentrum München – German Research Centre for Environmental Health), about 230 g of radioactive caesium-137 had been deposited over the Federal Republic of Germany.
In the long term, radioactive caesium is essentially taken up from the soil via the roots. Because radioactive caesium is strongly bound to certain clay minerals in the mineral soils of many arable fields, only negligible amounts reach the plants via the roots. Agricultural crops that were not sown or planted until after the Chernobyl reactor accident were therefore contaminated with only a few becquerels of radioactive caesium per kilogramme in the summer of 1986.
Protective measures
At the beginning of May 1986, the Commission on Radiation Protection recommended that only fresh milk with less than 500 becquerels of radioactive iodine-131 per litre be released for direct consumption. Some federal states applied much stricter standards and recommended, for example, that fresh milk with concentrations of radioactive iodine-131 above 20 becquerels per litre not be consumed.
The dairy farmers therefore disposed of milk from cows that had been fed on fresh pasture. They also ploughed contaminated outdoor vegetables under so that they could no longer be sold. The population avoided possibly contaminated foodstuffs such as seasonal outdoor vegetables.
(Closer) vicinity of Chornobyl power plant (1986)
The radiological situation in 1986 in the (immediate) vicinity of the Chornobyl nuclear power plant
Areas most affected by radioactive fallout from the 1986 Chornobyl accident were in
- Northern Ukraine,
- Belarus and
- Western Russia.
In particular, the immediate vicinity of the Chornobyl nuclear power plant was heavily contaminated by the reactor accident.
Protective measures/exclusion zone
In 1986, the area within a radius of 30 km around the Chornobyl nuclear power plant was established as an exclusion zone in order to protect the population from high levels of radiation. Places within the exclusion zone were evacuated. Among the communities affected were Prypyat, Chernobyl, and Kopachi. The exclusion zone was later adjusted based on the level of contamination.
Depending on the course of the accident, the prevailing wind directions, and subsequent clean-up and decontamination measures, the radioactive substances are distributed very unevenly within the exclusion zone.
The "Atlas of caesium deposition on Europe after the Chernobyl accident", a publication of the European Union in English and Russian, provides detailed map material on the distribution and deposition of caesium-137 in Europe and in the immediate vicinity of the Chornobyl nuclear power plant.
The situation today
Even today, more than three decades after the Chernobyl accident, the radiological situation in the (immediate) vicinity of the Chernobyl nuclear power plant and in Germany is very different:
Germany (today)
Current state of affairs: The radiological situation in Germany today
Of the radioactive substances released in the Chornobyl accident, only the long-lived caesium-137 is still relevant for the radiation to which humans and the environment are exposed (radiation exposure) in Germany and Central Europe. Because of its half-life of about 30 years, caesium-137 has decayed by slightly more than half from 1986 until today.
The radiation from caesium-137 to which people are exposed in Germany and Central Europe (e.g. through exposure from the outside or inhalation) can therefore be classified as low. The contamination of agriculturally produced foodstuffs with caesium-137, which is relevant for the uptake of the radionuclide with food, is also only minimal; only foodstuffs from the forest can still have increased levels of radioactive caesium-137.
Radioactive iodine-131 released from the reactor in Chornobyl in 1986 no longer plays a role because of its short half-life of 8 days; it has completely decayed.
Radioactive caesium in agricultural foodstuffs in Germany
Today, only low levels caesium-137 activity are found in domestically produced crops.
In Germany, there are no longer any radiologically relevant levels of radioactivity in agriculturally produced foodstuffs such as cereals, meat, or milk.
In mineral soil layers, such as those found on arable and pasture land, radioactive caesium is fixed by certain clay minerals contained in the soil and can thus be taken up only to a minimal extent by soil organisms and plant roots. Thus, more than 30 years after the accident, only low levels of caesium-137 activity can still be found in the crops produced in Germany. The content of caesium-137 in agricultural products from domestic production is now only a few becquerels per kilogram and below.
The result is that in Germany, less than 100 becquerels of caesium-137 per person and year are ingested on average with foodstuffs from agricultural production.
Current measurement results for agricultural products from domestic production (2020)
product | number of samples | minimum value | maximum value | mean value |
---|---|---|---|---|
milk (collection milk) | 804 | < 0,01 | 0,5 | 0,07 |
meat (beef, veal, pork, poultry) | 1.103 | < 0,04 | 12,9 | 0,2 |
leafy vegetables (outdoor cultivation) | 692 | < 0,02 | 2,4 | 0,1 |
fresh vegetables without leafy greens (outdoor cultivation) | 639 | < 0,02 | 0,4 | 0,08 |
potatoes | 236 | < 0,04 | 0,4 | 0,08 |
cereals | 666 | < 0,02 | 2,2 | 0,08 |
Limits for foodstuffs from trade in Germany
For commercially available foodstuffs in Germany, the limits for radiocaesium are as follows:
- 370 becquerels per kilogram for milk, milk products, and foodstuffs for infants and toddlers
- 600 becquerels per kilogram for all other foodstuffs.
Foodstuffs from German forests
Significantly elevated caesium-137 activities can still be measured in wild mushrooms and game, especially wild boar.
The situation for forest foodstuffs is quite different from the agricultural sector. Forest soils are characterised by organic layers on top of the mineral soils. In these layers, which are formed from decomposing litter and rich in soil organisms, radioactive caesium is readily available and is quickly taken up by soil organisms, fungi, and plants. It thus migrates only slowly into the mineral soil layers, where it can be fixed by certain clay minerals. The content of radioactive caesium in forest products therefore usually decreases only slowly.
Even today, more than three decades after the Chornobyl accident, significantly elevated caesium-137 activities can still be measured in foodstuffs from the forest such as edible mushrooms and game. A locally high fluctuation of the caesium-137 content is characteristic for wild mushrooms and game, especially wild boar.
Foodstuffs from the forests in the parts of Germany that were particularly affected by the Chornobyl fallout in 1986 – in particular the Bavarian Forest and the areas south of the Danube – have a higher level of contamination. There, forest products such as some edible mushroom species and wild boar meat sometimes still have caesium-137 levels of well over 100 becquerels per kilogram. In wild boar, well over 1,000 becquerels per kilogram, and in some cases even more than 10,000 becquerels per kilogram, are possible. In other regions (e.g. Northern Germany), the activity levels are much lower because of the lower deposition of radioactive caesium.
If you want to minimise your individual exposure to radiation, you should limit – or even eliminate – the consumption of wild mushrooms that you have picked yourself and game that you have shot yourself (especially wild boar) from the Bavarian Forest and other highly contaminated areas in Southern Germany.
Wood from Southern Germany, which was more severely affected by the accident in Chernobyl, can have caesium-137 activities of up to several 100 becquerels per kilogram.
More forest products from Germany
Wood from southern Germany, which was more severely affected by the reactor accident in Chornobyl, can have caesium-137 activities of up to several 100 becquerels per kilogram.
In the case of wood products such as furniture or parquet flooring, the radiation to which people are exposed is only minimal – as is the case for firewood burnt in an open fireplace or wood pellets used in boilers in private households. However, because caesium-137 remains mainly in the ash, this should not be used to fertilise vegetable beds in private gardens just to remain on the safe side.
As long as no large quantities of wood are burnt in biomass power plants in Germany, monitoring of the radioactivity content of the wood ash (or the proper disposal thereof) is not important from a radiation protection point of view.
(Closer) vicinity of Chornobyl power plant (today)
Current state of affairs: The radiological situation in the vicinity of the Chornobyl nuclear power plant today
Dilapidated building in the abandoned city of Prypyat – in the foreground, a measuring device for gamma radiation.
Radioactive caesium and strontium as well as transuranic elements such as plutonium and americium can still be found in the immediate vicinity of the Chornobyl nuclear power plant. In 1986, in the town of Prypyat, about 3 kilometres north west of the Chernobyl nuclear power plant, up to:
- 24 megabecquerels per square metre of caesium-137
- 6.7 megabecquerels per square metre of strontium-90
- 0.2 megabecquerels per square metre plutonium-239/240
were deposited (among others). Despite decontamination measures, the radiation to which people and the environment are exposed is still so high that the city cannot be inhabited.
The half-lives of the radionuclides deposited provide an indication of the current exposure.
- Caesium-137 and strontium-90 (with half-lives of about 30 and 29 years, respectively) have decayed by slightly more than half to date. The deposited activities of these radionuclides have thus also been roughly halved.
- Plutonium-239 and plutonium-240 have half-lives of several thousand years (plutonium-239: about 24,000 years; plutonium-240: about 6,600 years) and americium-241 about 430 years. These radioactive substances have thus practically not decayed at all – their activities are about the same as they were in 1986.
Warning sign at the entrance to the exclusion zone around the damaged Chornobyl nuclear power plant - unauthorised access to the zone is prohibited.
On the Belarusian side, a protected area was added to the Ukrainian exclusion zone around the Chornobyl nuclear power plant since 1988. Over the years, the boundaries of the exclusion zone have been adjusted according to the contamination situation. Access to both exclusion areas is allowed only with a permit.
Elevated radiation levels are still present in the Chornobyl exclusion zone. The contamination from the reactor accident and the radiation levels (ambient dose rate) are considerably higher than those in Germany.
Agricultural foodstuffs in Ukraine
In 1990, the Federal Office for Radiation Protection carried out measurements on agricultural foodstuffs in Kiev on behalf of the Foreign Office. These did not reveal any significantly elevated caesium-137 contamination levels on the foodstuffs investigated.
Foodstuffs from state production and foodstuffs sold in public shops (e.g. supermarkets) are subject to state control. Comparatively restrictive limits apply to the content of radionuclides in these goods.
Foodstuffs from non-controlled sources (e.g. from market or street stalls) may have elevated levels of contamination.
Foodstuffs from Ukrainian and Belarusian forests
Higher activities of caesium-137 can occur in mushrooms, wild berries, and game in Ukraine and Belarus. The more the area in question was contaminated with radioactive caesium, the higher the content of this radionuclide.
Especially in the more highly contaminated areas of Ukraine and Belarus, foodstuffs from the forest (e.g. game, wild berries, and wild mushrooms) can be extremely contaminated with radioactive caesium.
Fisch from standing waters in Ukraine and Belarus
Freshwater fish from stagnant waters or waters with little water exchange can be highly contaminated with radioactive strontium. This particularly affects the areas that have been heavily contaminated by radioactive strontium.
Measurement of the ambient dose rate with a handheld measuring device at the Chornobyl reactor as part of a measurement exercise in 2016. At the time of the accident, the measured values were much higher.
What should be kept in mind when visiting Belarus, Ukraine, and especially the immediate vicinity of the Chornobyl nuclear power plant?
Large parts of Belarus and Ukraine were no more highly contaminated with highly volatile radioactive substances (e.g. caesium-137, which dispersed with the wind and weather) than the more severely affected areas of Germany.
However, the immediate vicinity of the Chornobyl nuclear power plant, especially the exclusion zone, can still be extremely contaminated. In particular, non-volatile, long-lived radioactive substances (e.g. plutonium and americium) were deposited in the immediate vicinity of the Chernobyl nuclear power plant.
From a radiation protection perspective, the inhalation of radionuclides emitting alpha radiation is particularly relevant – as is the high, strongly varying external radiation exposure resulting from deposited radioactive substances (ambient dose rate).
Sightseeing in Chornobyl as well as in the exclusion zone around the damaged reactorShow / Hide
The Federal Office for Radiation Protection advises against visiting the highly contaminated areas, especially in the exclusion zone around the Chornobyl nuclear power plant, for tourism reasons.
Within the exclusion zone, the radiation to which people are exposed through deposited radioactive substances (external radiation exposure) can vary considerably. Locally, external radiation exposure of several 10 microsieverts per hour and more can be expected. For comparison: In Germany, this value is between 0.05 and 0.18 microsieverts per hour.
Danger from absorption of radioactive particles into the body
In addition to external radiation exposure from deposited radioactive substances, people in the exclusion zone are also at risk of absorbing highly radioactive particles into their bodies (incorporation) – for example, by inhaling dust to which radioactive particles adhere. Weather conditions such as drought or storms (in which dust is stirred up and can thus be inhaled) are particularly unfavourable.
Transuranics such as plutonium-239, plutonium-240, or americium-241 are radioactive and emit alpha radiation. If they are inhaled, this can lead to high radiation exposures of the airways and lungs depending on the type and amount of radionuclides inhaled.
Radionuclides can also enter the human body unintentionally (e.g. through dirty hands).
Necessary short occupational stays in the exclusion zone around the damaged reactorShow / Hide
The Federal Office for Radiation Protection advises against any unnecessary stay in the highly contaminated areas surrounding the Chornobyl nuclear power plant, especially in the exclusion zone.
Safety precautions for unavoidable stays
BfS staff during a measuerement exercise in the exclusion zone near Chernobyl.
However, if a stay in the exclusion zone is necessary, for example for professional reasons, at least the following safety precautions should be taken to protect against radiation:
- Continuously measure external radiation exposure with suitable measuring devices with warning function
- Minimise unintentional absorption of radionuclides into the body through your own behaviour (do not touch anything, do not eat, do not drink)
- Protect yourself against the inhalation of alpha-emitting radionuclides (wear respiratory protection if stirring up contaminated soil cannot be ruled out because of weather conditions)
- Have yourself checked for radioactive contamination (and decontaminated if necessary) when leaving the exclusion zone
It is important to ensure that all of the above safety precautions are observed.
Reliable information on the level of external radiation exposure resulting from deposited radioactive substances (ambient dose rate) can be obtained only if a suitable measuring device is worn during the entire stay. Radiation exposure from radioactive substances that enter the human body through the breath or mouth cannot be detected by such a measuring device.
Note
When entering the exclusion zone, high-dose iodine tablets for iodine thyroid blocking should not be taken. The radioactive iodine-131 released in the 1986 accident has long since decayed, and the unnecessary intake of high amounts of iodine could have negative health consequences.
Longer stays in Belarus and Ukraine outside the exclusion zone around the Chornobyl nuclear power plantShow / Hide
From a radiation protection perspective, people can travel to Russia, Belarus, or Ukraine without hesitation – even for prolonged periods of time. Large parts of Belarus and Ukraine were not more highly contaminated than the more severely affected areas of Germany. There is no need for radiation protection measures.
The only exception is the more heavily contaminated areas (especially the exclusion zone) in the vicinity of the Chornobyl nuclear power plant.
Hints and tips for behaviour for stays outside the exclusion zone
Foodstuffs that come from state production or which are sold in public shops (for example supermarkets) are subject to state control. In a 2006 publication, the Chornobyl Forum confirms that the – comparatively restrictive – limits for radioactivity were not exceeded during checks on these goods. The Chornobyl Forum is a consortium of international organisations and the competent authorities of Ukraine, Belarus, and the Russian Federation.
The consumption of foodstuffs from non-controlled sources (e.g. from market or street stalls) should be avoided. Especially in the more highly contaminated areas of Ukraine and Belarus, foodstuffs from the forest (game, wild berries, and wild mushrooms) should be avoided because these can be extremely contaminated with radioactive caesium. Freshwater fish of unknown origin should also not be consumed because they may be highly contaminated with radioactive strontium.
What was the situation before 26 April 1986?
Daily intake of caesium-137, caesium-134 and strontium-90 with the total diet in becquerel per person and day
In Germany, systematic measurements, especially of radioactive caesium and strontium, in various environmental media began in the late 1950s.
The Federal Institute of Nutrition (now the Max Rubner Institute, Federal Research Institute of Nutrition and Food) observed a steep increase in the activity levels of the measured radionuclides in all animal and plant foods until 1964; this was due to the fallout from above-ground nuclear weapons tests.
The relatively rapid decline until 1970 can be explained by the decrease in the direct deposition of radioactive substances from the tests on plants as a result of the ban on above-ground nuclear weapons testing. After that, the activity levels in the diet decreased continuously. In 1986, the Chernobyl fallout significantly increased contamination levels again after 26 April 1986.
State of 2022.04.12