), or radiocaesium, is a radioactive isotope of caesium that is formed as one of the more common fission products by the nuclear fission of uranium-235 and other fissionable isotopes in nuclear reactors and nuclear weapons. Trace quantities also originate from natural fission of uranium-238. It is among the most problematic of the short-to-medium-lifetime fission products. 137Cs has a relatively low boiling point (671 °C, 1240 F) and is volatilized easily when released suddenly at high temperature, as in the case of the Chernobyl nuclear accident and with atomic explosions, and can travel very long distances in the air. After being deposited onto the soil as radioactive fallout, it moves and spreads easily in the environment because of the high water solubility of caesium's most common chemical compounds, which are salts. 137Cs was discovered by Glenn T. Seaborg and Margaret Melhase.
|Natural abundance||0 (trace)|
|Half-life||30.17 y ± 0.03 y|
|Parent isotopes||137Xe (β−)|
|Isotope mass||136.907 u|
|Decay mode||Decay energy (MeV)|
|β- (beta decay)||0.5120|
|Isotopes of caesium |
Complete table of nuclides
Caesium-137 has a half-life of about 30.17 years. About 94.6% decays by beta emission to a metastable nuclear isomer of barium: barium-137m (137mBa, Ba-137m). The remainder directly populates the ground state of barium-137, which is stable. Metastable barium has a half-life of about 153 seconds, and is responsible for all of the gamma ray emissions in samples of caesium-137. 137mBa decays to the ground state by emission of photons having energy 0.6617 MeV. A total of 85.1% of 137Cs decays lead to gamma ray emission in this way. One gram of caesium-137 has an activity of 3.215 terabecquerel (TBq).
Caesium-137 has a number of practical uses. In small amounts, it is used to calibrate radiation-detection equipment. In medicine, it is used in radiation therapy. In industry, it is used in flow meters, thickness gauges, moisture-density gauges (for density readings, with americium-241/beryllium providing the moisture reading), and in gamma ray well logging devices.
Caesium-137 is not widely used for industrial radiography because it is hard to obtain a very high specific activity material with a well defined (and small shape) as caesium from used nuclear fuel contains stable caesium and also long lived Cs-135. Also the higher specific activity caesium sources tend to be made from very soluble caesium chloride (CsCl), as a result if a radiography source was damaged it would increase the spread of the contamination. It is possible to make water insoluble caesium sources (with various ferrocyanide compounds such as Ni
6, and ammonium ferric hexacyano ferrate (AFCF), Giese salt, ferric ammonium ferrocyanide) but their specific activity will be much lower. A large emitting volume will harm the image quality in radiography. Iridium-192 and cobalt-60, 60
, are preferred for radiography, since these are chemically non-reactive metals and can be obtained with much higher specific activities by the activation of stable cobalt or iridium in high flux reactors.
As an almost purely man-made isotope, caesium-137 has been used to date wine and detect counterfeits and as a relative-dating material for assessing the age of sedimentation occurring after 1945.
Caesium-137 is also used as a radioactive tracer in geologic research to measure soil erosion and deposition.
Health risk of radioactive caesiumEdit
Caesium-137 reacts with water, producing a water-soluble compound (caesium hydroxide). The biological behaviour of caesium is similar to that of potassium and rubidium. After entering the body, caesium gets more or less uniformly distributed throughout the body, with the highest concentrations in soft tissue.: 114 The biological half-life of caesium is about 70 days.
A 1961 experiment showed that mice dosed with 21.5 μCi/g had a 50% fatality within 30 days (implying an LD50 of 245 μg/kg). A similar experiment in 1972 showed that when dogs are subjected to a whole body burden of 3800 μCi/kg (140 MBq/kg, or approximately 44 μg/kg) of caesium-137 (and 950 to 1400 rads), they die within 33 days, while animals with half of that burden all survived for a year. Important researches have shown a remarkable concentration of 137Cs in the exocrine cells of the pancreas, which are those most affected by cancer. In 2003, in autopsies performed on 6 children dead in the polluted area near Chernobyl where they also reported a higher incidence of pancreatic tumors, Bandazhevsky found a concentration of 137Cs 40-45 times higher than in their liver, thus demonstrating that pancreatic tissue is a strong accumulator and secretor in the intestine of radioactive cesium.
Accidental ingestion of caesium-137 can be treated with Prussian blue (FeIII
3), which binds to it chemically and reduces the biological half-life to 30 days.
Radioactive caesium in the environmentEdit
Caesium-137, along with other radioactive isotopes caesium-134, iodine-131, xenon-133, and strontium-90, were released into the environment during nearly all nuclear weapon tests and some nuclear accidents, most notably the Chernobyl disaster and the Fukushima Daiichi disaster.
Caesium-137 in the environment is substantially anthropogenic (human-made). Caesium-137 is produced from the nuclear fission of plutonium and uranium, and decays into barium-137. Before the construction of the first artificial nuclear reactor in late 1942 (the Chicago Pile-1), caesium-137 had not occurred on Earth in significant amounts for about 1.7 billion years. By observing the characteristic gamma rays emitted by this isotope, one can determine whether the contents of a given sealed container were made before or after the first atomic bomb explosion (Trinity test, 16 July 1945), which spread some of it into the atmosphere, quickly distributing trace amounts of it around the globe. This procedure has been used by researchers to check the authenticity of certain rare wines, most notably the purported "Jefferson bottles". Surface soils and sediments are also dated by measuring the activity of 137Cs.
As of today and for the next few hundred years or so, caesium-137 and strontium-90 continue to be the principal source of radiation in the zone of alienation around the Chernobyl nuclear power plant, and pose the greatest risk to health, owing to their approximately 30 year half-life and biological uptake. The mean contamination of caesium-137 in Germany following the Chernobyl disaster was 2000 to 4000 Bq/m2. This corresponds to a contamination of 1 mg/km2 of caesium-137, totaling about 500 grams deposited over all of Germany. In Scandinavia, some reindeer and sheep exceeded the Norwegian legal limit (3000 Bq/kg) 26 years after Chernobyl. As of 2016, the Chernobyl caesium-137 has decayed by half, but could have been locally concentrated by much larger factors.
Fukushima Daiichi disasterEdit
In April 2011, elevated levels of caesium-137 were also being found in the environment after the Fukushima Daiichi nuclear disasters in Japan. In July 2011, meat from 11 cows shipped to Tokyo from Fukushima Prefecture was found to have 1,530 to 3,200 becquerels per kilogram of 137Cs, considerably exceeding the Japanese legal limit of 500 becquerels per kilogram at that time. In March 2013, a fish caught near the plant had a record 740,000 becquerels per kilogram of radioactive caesium, above the 100 becquerels per kilogram government limit. A 2013 paper in Scientific Reports found that for a forest site 50 km from the stricken plant, 137Cs concentrations were high in leaf litter, fungi and detritivores, but low in herbivores. By the end of 2014, "Fukushima-derived radiocaesium had spread into the whole western North Pacific Ocean", transported by the North Pacific current from Japan to the Gulf of Alaska. It has been measured in the surface layer down to 200 meters and south of the current area down to 400 meters.
Caesium-137 is reported to be the major health concern in Fukushima. A number of techniques are being considered that will be able to strip out 80% to 95% of the caesium from contaminated soil and other materials efficiently and without destroying the organic material in the soil. These include hydrothermal blasting. The caesium precipitated with ferric ferrocyanide (Prussian blue) would be the only waste requiring special burial sites. The aim is to get annual exposure from the contaminated environment down to 1 mSv above background. The most contaminated area where radiation doses are greater than 50 mSv/year must remain off limits, but some areas that are currently less than 5 mSv/year may be decontaminated, allowing 22,000 residents to return.
Incidents and accidentsEdit
Caesium-137 gamma sources have been involved in several radiological accidents and incidents.
1987 Goiânia, Goiás, BrazilEdit
In the Goiânia accident of 1987, an improperly disposed of radiation therapy system from an abandoned clinic in Goiânia, Brazil, was removed then cracked to be sold in junkyards, and the glowing caesium salt sold to curious, unadvised buyers. This led to four confirmed deaths and several serious injuries from radiation contamination. Caesium gamma-ray sources that have been encased in metallic housings can be mixed in with scrap metal on its way to smelters, resulting in production of steel contaminated with radioactivity.
1989 Kramatorsk, Donetsk, UkraineEdit
The Kramatorsk radiological accident happened in 1989 when a small capsule containing highly radioactive caesium-137 was found inside the concrete wall of an apartment building in Kramatorsk, Ukrainian SSR. It is believed that the capsule, originally a part of a measurement device, was lost in the late 1970s and ended up mixed with gravel used to construct the building in 1980. Over 9 years, two families had lived in the apartment. By the time the capsule was discovered, 6 residents of the building had died from leukemia and 17 more had received varying doses of radiation.
In 1997, several Georgian soldiers suffered radiation poisoning and burns. They were eventually traced back to training sources abandoned, forgotten, and unlabeled after the dissolution of the Soviet Union. One was a caesium-137 pellet in a pocket of a shared jacket that put out about 130,000 times the level of background radiation at 1 meter distance.
1998, Los Barrios, Cádiz, SpainEdit
2009 Tongchuan, Shaanxi, ChinaEdit
In 2009, a Chinese cement company (in Tongchuan, Shaanxi Province) was demolishing an old, unused cement plant and did not follow standards for handling radioactive materials. This caused some caesium-137 from a measuring instrument to be included with eight truckloads of scrap metal on its way to a steel mill, where the radioactive caesium was melted down into the steel.
March 2015, University of Tromsø, NorwayEdit
In March 2015, the Norwegian University of Tromsø lost 8 radioactive samples including samples of caesium-137, americium-241, and strontium-90. The samples were moved out of a secure location to be used for education. When the samples were supposed to be returned the university was unable to find them. As of 4 November 2015[update] the samples are still missing.
March 2016 Helsinki, Uusimaa, FinlandEdit
On 3 and 4 March 2016, unusually high levels of caesium-137 were detected in the air in Helsinki, Finland. According to STUK, the country's nuclear regulator, measurements showed 4,000 μBq/m3 — about 1,000 times the usual level. An investigation by the agency traced the source to a building from which STUK and a radioactive waste treatment company operate.
May 2019 Seattle, Washington, USEdit
Thirteen people were exposed to caesium-137 in May 2019 at the Research and Training building in the Harborview Medical Center complex. A contract crew was transferring the caesium from the lab to a truck when the powder was spilled. Five people were decontaminated and released, but 8 who were more directly exposed were taken to the hospital while the research building was evacuated.
- National Institute of Standards and Technology (6 September 2009). "Radionuclide Half-Life Measurements". Retrieved 7 November 2011.
82". WWW Table of Radioactive Isotopes. LBNL Isotopes Project - LUNDS Universitet. Archived from the original on 22 May 2015. Retrieved 14 March 2009.
- Delacroix, D.; Guerre, J. P.; Leblanc, P.; Hickman, C. (2002). Radionuclide and Radiation Protection Handbook. Nuclear Technology Publishing. ISBN 978-1870965873.
- Bunting, R. L. (1975). "Nuclear Data Sheets for A=137". Nuclear Data Sheets 15. 335.
- "CDC Radiation Emergencies | Radioisotope Brief: Cesium-137 (Cs-137)". CDC. Retrieved 5 November 2013.
- "Cesium | Radiation Protection | US EPA". EPA. 3 June 2012. Archived from the original on 6 September 2015. Retrieved 4 March 2015.
- "How Atomic Particles Helped Solve A Wine Fraud Mystery". NPR. 3 June 2014. Retrieved 4 March 2015.
- Williams, H. F. L. (1995). "Assessing the impact of weir construction on recent sedimentation using cesium-137". Environmental Geology. 26 (3): 166–171. Bibcode:1995EnGeo..26..166W. doi:10.1007/BF00768738. ISSN 0943-0105. S2CID 129177016.
- Loughran, Robert (1 June 1989). "The measurement of soil erosion". Progress in Physical Geography. 221 (2): 216–233. doi:10.1177/030913338901300203. S2CID 140599684.
- Avery, Simon V. (1995). "Caesium accumulation by microorganisms: uptake mechanisms, cation competition, compartmentalization and toxicity". Journal of Industrial Microbiology. 14 (2): 76–84. doi:10.1007/BF01569888. ISSN 0169-4146. PMID 7766213. S2CID 21144768.
- Delacroix, D.; Guerre, J. P.; Leblanc, P.; Hickman, C. (2002). Radionuclide and Radiation Protection Data Handbook 2002 (2nd ed.). Nuclear Technology Publishing. ISBN 978-1-870965-87-3.
- R. Nave. "Biological Half-life". Hyperphysics.
- Moskalev, Yu. I. (1961). "Biological Effects of Cesium-137". In Lebedinskiĭ, A. V.; Moskalev, Yu. I. (eds.). Distribution, Biological Effects, and Migration of Radioactive Isotopes. Translation Series. United States Atomic Energy Commission (published April 1974). p. 220. AEC-tr-7512.
- H.C. Redman; et al. (1972). "Toxicity of 137-CsCl in the Beagle. Early Biological Effects". Radiation Research. 50 (3): 629–648. Bibcode:1972RadR...50..629R. doi:10.2307/3573559. JSTOR 3573559. PMID 5030090.
- Nelson A , Ullberg S, Kristoffersson H, Ronnback C (1961). "Distribution of Radiocesium in Mice". Acta Radiologica. 55, 5 (5): 374–384. doi:10.3109/00016926109175132. PMID 13728254.CS1 maint: multiple names: authors list (link)
- Venturi, Sebastiano (2020). "Correlation between radioactive cesium and the increase of pancreatic cancer: A Hypothesis". Biosfera. 12, (4) (4): 21–30.
- Bandazhevsky Y.I. (2003). "Chronic Cs-137 incorporation in children's organs". Swiss Med. Wkly. 133 (35–36): 488–90. PMID 14652805.
- "CDC Radiation Emergencies | Facts About Prussian Blue". CDC. Archived from the original on 20 October 2013. Retrieved 5 November 2013.
- Takeshi Okumura (21 October 2003). "The material flow of radioactive cesium-137 in the U.S. 2000" (PDF). epa.gov/. US Environmental Protection Agency.
- Peter Hellman; Mitch Frank (1 April 2010). "News Analysis: Christie's Is Counterfeit Crusader's Biggest Target". Wine Spectator. Retrieved 5 November 2013.
- Sandelson, Michael; Smith, Lyndsey (21 May 2012). "Higher radiation in Jotunheimen than first believed". The Foreigner. Archived from the original on 2 October 2018. Retrieved 21 May 2012.
- "High levels of caesium in Fukushima beef". Independent Online. 9 July 2011.
- "Fish near Fukushima reportedly contains high Cesium level". Huffington Post. 17 March 2013.
- Murakami, Masashi; Ohte, Nobuhito; Suzuki, Takahiro; Ishii, Nobuyoshi; Igarashi, Yoshiaki; Tanoi, Keitaro (2014). "Biological proliferation of cesium-137 through the detrital food chain in a forest ecosystem in Japan". Scientific Reports. 4: 3599. Bibcode:2014NatSR...4E3599M. doi:10.1038/srep03599. ISSN 2045-2322. PMC 3884222. PMID 24398571.
- Kumamoto, Yuichiro; et al. (2017). "Radiation and analytical chemistry – Five years since the Fukushima Daiichi nuclear power plant accident". Special Articles. Bunseki Kagaku (in Japanese and English). 66 (3): 137–148. doi:10.2116/bunsekikagaku.66.137.
- Normile, Dennis (1 March 2013). "Cooling a hot zone". Science. 339 (6123): 1028–1029. Bibcode:2013Sci...339.1028N. doi:10.1126/science.339.6123.1028. PMID 23449572.
- Hill, Kyle (4 September 2021). "How one handful of powder contaminated a whole city". YouTube. Retrieved 26 September 2021.
- The Radiological Accident in Goiânia (PDF). IAEA. 1988. ISBN 92-0-129088-8.
- "Vítima do césio-137 lembra depressão e preconceito após acidente". BBC Brasil. 26 April 2011.
- "Radioactive Scrap Metal". Nuclear Free Local Authorities. October 2000. Archived from the original on 21 March 2007.
- "Infected Apartment in Kramatorsk | Series 'The most radioactive zones on the planet' | OrangeSmile.com". www.orangesmile.com.
- Lluma, Diego (May–June 2000). "Former Soviet Union: What the Russians left behind". Bulletin of the Atomic Scientists. 56 (3): 14–17. doi:10.2968/056003005.
- J.M. LaForge (1999). "Radioactive Caesium Spill Cooks Europe". Earth Island Journal. 14 (1). Archived from the original on 5 September 2008. Retrieved 28 March 2009.
- "Chinese 'find' radioactive ball". BBC News. 27 March 2009.
- "UiT har mistet radioaktivt stoff – kan ha blitt kastet". iTromsø. 4 November 2015.
- "Stort metallskap sporløst forsvunnet. Inneholder radioaktive stoffer". Dagbladet. 4 November 2015.
- "Cesium 137 now traced back to the property's garage and parts of its basement premises - Tiedote-en - STUK". www.stuk.fi. Retrieved 10 March 2016.
- Hannele Aaltonen. "Cesium-137 contamination at STUK's premises in March 2016" (PDF). IAEA. Retrieved 13 October 2018.
- Casey Martin (3 May 2019). "13 exposed to radioactivity". KUOW.
- Olsen, Rolf A. (1994). "4.2. The Transfer of Radiocaesium from Soil to Plants and Fungi in Seminatural Ecosystems". Nordic Radioecology - the Transfer of Radionuclides through Nordic Ecosystems to Man. Studies in Environmental Science. 62. pp. 265–286. doi:10.1016/S0166-1116(08)71715-1. ISBN 9780444816177.