The good news:
If the roof had fallen in the summer, the radioactive dust would be instantly sold on for miles, but in the current winter weather radioactive dust can threaten only workers NPP, so far ...
The bad news:
Dropped inside the sarcophagus water from melting snow can dramatically increase the radioactivity of the fuel rods:
Water, under the sarcophagus is a source of several kinds of dangers:
- falling on the accumulation of fuel-containing materials, it leads to an increase in the effective neutron multiplication factor in the system;
- water slowly destroys the fuel, and contributes to the uncontrolled movement of radioactivity in the inner rooms and the removal of radionuclides beyond the "Shelter";
- transferring the dissolved salts of enriched uranium, the water can increase the potential danger of a nuclear Object;
- water promotes corrosion destruction of building constructions "Shelter".
- it prevents research to improve the electrical safety of object;
- water violates the normal operation of diagnostic systems. After strong rains have taken place 2 "anomalous" neutron events (significant increase generation of neutrons) recorded by 12 and 16 September 1996. Neutron radiation, which initially increased, after spraying with a solution of gadolinium decreased to usual levels [Official website: Institute of Problems of Safe Development of Nuclear Energy http://www.ibrae.ac.ru/].
Chernobyl experience
Post-Accident Management
Building the Chernobyl "sarcophagus" (object "Shelter") was necessary to reduce emissions of radioactive substances from the fragments 4 reactor. The main reason of problems is the use of temporary structure as permanent [1-2].
Previously in the "clean" area were tested methods of remote connection of large constructions, remote control for concrete pumping equipment, designed a system of television and radio construction control, created special cabins-capsules that allow visually inspect poorly accessible places with the help of cranes. To reducethe overall level of radiation dose was shot and buried radioactive ground, fragments of building constructions and equipment from the area around the reactor, after which the entire area was covered with a layer of gravel and sand thickness of 50 cm and a concrete layer. At this concreting had spent more than 100 000 cubic meters of concrete. [3]
For building of the Chernobyl sarcophagus been used elements of Block 4 destroyed by reactor explosion. This was done to reduce construction period (6 months). But even this variant required the use of more than 200 000 tons of concrete and more than 10 000 tons of steel. The principal disadvantages of this approach are:
- huge collective dose of radiation exposure obtained by builders and fitters;
- necessity to build new structures very close to destroyed reactor in large radiation fields;
- impossibility to fit exactly to each other large metal structures by using remote installation;
- impossibility to assess residual strength of structures after an explosion and fire;
- large masses of concrete were not included in the designated area because of the
imperfections of remote methods of concreting;
- flow of concrete in the damaged areas have limited access to them;
- impossibility accurate and precise work near a strong source of radiation has led to the main
problem of construction - leakage;
- total cracks area was estimated as 1000 square meters. [4-8]
Through the holes every year leaks around 2000 cubic meters of water, which eventually coalesce at rooms of the lower level Block 4. Yearly volumes of condensate at Block 4 is about 1650 cubic meters. The 180 cubic meters/year are the remnants spray for dust suppression. All of this water passes through the debris Block 4 and is going to basement rooms. Every year about 2100 cubic meters of collected water evaporates, and about 1300 cubic meters seeps through the foundation at ground under the Block 4 [9].
Water, under the sarcophagus is a source of several kinds of dangers:
- falling on the accumulation of fuel-containing materials, it leads to an increase in the effective neutron multiplication factor in the system;
- water slowly destroys the fuel, and contributes to the uncontrolled movement of radioactivity in the inner rooms and the removal of radionuclides beyond the "Shelter";
- transferring the dissolved salts of enriched uranium, the water can increase the potential danger of a nuclear Object;
- water promotes corrosion destruction of building constructions "Shelter".
- it prevents research to improve the electrical safety of object;
- water violates the normal operation of diagnostic systems. After strong rains have taken place 2 "anomalous" neutron events (significant increase generation of neutrons) recorded by 12 and 16 September 1996. Neutron radiation, which initially increased, after spraying with a solution of gadolinium decreased to usual levels [2].
Carried out in 1995 - 1997 years studies have shown that the main source of water pollution by 90Sr are oxidised fuel particles U3O8. Their rate of dissolution is much higher than that of the fuel particles UO2.
In the first moments of the accident takes place the destruction of the fuel tablets of uranium dioxide on grain boundaries. During the Chernobyl accident was found that the over time takes place crushing large particles at a more dangerous form for humans [10-14].
Because of the possibility of the collapse of the "Shelter" and the release of radioactive dust into the environment, under the roof was installed dust suppression system, which periodically spray dust suppression solutions. This system has been in operation since 1990, and during this time it was sprayed over 1000 tons of solutions [15].
After the accident comparable with Chernobyl, finely dispersed solid radioactive substances can penetrate into the constructions at a depth of several cm, and the radioactive water at cement screed, plaster, brick at a depth of 10 cm or more. Repeated treatment of decontamination solutions does not usually lead to lower radiation dose rate to acceptable levels. To reduce the level of radiation, it is necessary to cover the surface by lead.
During the Chernobyl accident, the best medical care was assisted for KGB officers. Techniques of enterosorbtion by zeolite and hemodialysis with activated carbon proved their efficiency for removing of radionuclides from the body. Studies have shown that the amount of radionuclides in the body can be reduced by 3-4 times before they produce significant internal exposure [16-20].
Enough quality, to protect from external radiation and radioactive dust, nowadays have only spacesuits for astronauts. For the work at nuclear power plants are most suitable Hard-shell suits. However, they are very heavy and it is necessary to movement a mobile bigger vehicle for one person.
Among other space-based technology may be useful robot arm for different manipulations.
The most expensive and most universal way to protect and cool the reactor is filling it by Indium (In). Indium's high neutron capture cross section for thermal neutrons makes it suitable for use in control rods for nuclear reactors, typically in an alloy containing 80% Silver, 15% Indium, and 5% Cadmium [21-27] In the reactor, together with the indium, need to place thermoelectric elements (based on the Peltier effect) as a coolers. All other variants of cooling require mass transfer of cooling fluid. Radioactive water at the reactor is best to use for the concreting of the internal spaces. In the absence of information about the location of molten uranium fuel, it is better in the water and concrete solutions add boron compounds (B4C for example).
For fast cutting armature rubble, and welding sections of new constructions is best to use plasma torches. Cracks will be formed in construction in any case. The main task is the localization of cracks. In laminated structures, cracks increase mostly within the layer. It must be a sufficient viscosity of the material to resist earthquakes and radiation embrittlement. Lead is consistent most of the requirements. Supporting function should be assigned on the welded, not removable formwork of stainless steel. All other options require additional corrosion protection, which near the source of radiation is difficult to make. The design should be formed layer by layer of lead and concrete. To prevent the formation and movement of radioactive dust by wind, all external surfaces of buildings must be made of steel. Protective structures of steel and concrete, lead, will have considerable weight, and therefore need more support construction for the roof. Temporarily this function can perform reliably fixed crane. On the crane line, fixing the building, must be mounted dampers for the localization of vibrations during earthquakes. It is necessary to mount geodetic marks which allow to determine the sediment and deformation structures in time. For the isolation of radioactive groundwater is necessary under the base lay several layers of rubber. This is usually made by an underground cutter with large number water cutting nozzles. However, all existing models of such units are small in size and are designed for small depth (few meters). To create the underground layers of rubber or heat-resistant materials under nuclear power plants need to design an exclusive technology.
References
1. USSR State Committee on the Utilisation of Atomic Energy "The Accident at the Chernobyl
NPP and its Consequences" IAEA Post Accident Review Meeting, Vienna, 25-29 August 1986.
2. Official website: Institute of Problems of Safe Development of Nuclear Energy
http://www.ibrae.ac.ru/
3. A.R.Sich. “Chernobyl Accident Management Actions”, Nuclear Safety, Vol.35, N1, Janusry-
June 1994
4. "Policy Statement on Regulation of Nuclear and Radiation Safety of"Shelter "on Chernobyl
nuclear power plant. Approved by the Ministerial Order of 08.04.1998, № 49
5. "Analysis of the current safety of the Shelter and forecasts of the situation. " Ans. Artist
Borovoy A.A. Report of ISTC "Shelter ", arch. № 3836
6. Borovoy A.A., Bogatov S.A., Pazukhin E.M. "The current state of the Shelter and its impact on
the environment" / Radiochemistry. - T.41, № 4, 1999
7. Borovoy A.A., Evstratenko A.S., Krinitsyn A.P. et al "Dynamics of the radiation situation at
the"Shelter" object": - 10 years, the main results of scientific research / National Academy of
Sciences of Ukraine. - Chernobyl, 1996
8. Borovoy A.A., Gorbachev B.I., Evstratenko A.S. et al. "aerosol pollution of the Shelter and
submicron aerosols. Collection " Problems of Chernobyl / ISTC NAS. Issue 15. Chernobyl 2004
9. ENVIRONMENTAL IMPACT ASSESSMENT, New Safe Confinement Conceptual Design:
Chernobyl Nuclear Power Plant – Unit 4. State Specialised Enterprise Chernobyl Nuclear Power
Plant, Kiev 2003
10. Bar'yakhtar V.G. Biiky A.A. Borovoy A.A., Karasev B.C. Sarcophagus of today and tomorrow
Kiev, 1992. - S. 1 - 19. - Preprint, Ukrainian Academy of Sciences.
11. Description of the "Shelter" and requirements for its transformation: Report IAE them. IV
Kurchatov Complex expedition; VNIPIET. - Chernobyl, 1991
12. Dushin V.N., Petrov, B.F., Pleskachevsky L.A., and G.S. Boykov, Evdokimov I.V., Korostin
I.Y., Naydenov E.G., Prusakov A.G., Sokolov A.M., Ibraimov G.D., Checherov K.P. "Localization of
sources of intense gamma rays and evaluation of fuel in the Central Hall of the 4-th unit of Chernobyl.
" NPO "Radium Institute ", Inv. № 1732 and, Chernobyl in 1992
13. Usatyj A.F. Generalized results of determination of distributions of major gamma radiation
sources in the central hall of the Sarcophagus, recorded by dosimetric cords using EPR sensors. In:
“Sarcophagus Safety’94”. The State of Chernobyl Nuclear Power Plant Unit 4. Proceedings of an
International Symposium. Zeleney Mys, Ukraine, 14-18 March 1994
14. Borovoi А.А. Analytical Report ( Post- Accident Management of Destroyed Fuel from
Chernobyl ) //IAEA, Work Material, 1990
15. Borovoi А.А., Object "Shelter" Safety Analysis Report 2001
16. Official website: Security Service of Ukraine (In 1986 Ukrainian Department KGB USSR)
http://www.sbu.gov.ua/sbu/control/uk/publish/article?art_id=48991
17. S.V. Mikhalovsky and V.G. Nikolaev Interface Science and Technology., Activated Carbon
Surfaces in Environmental Remediation: Chapter 11 Activated carbons as medical adsorbents V. 7, 2006
18. Patrick J. Faustino et. al. Quantitative determination of cesium binding to ferric
hexacyanoferrate: Prussian blue., Journal of Pharmaceutical and Biomedical Analysis V. 47, Issue 1., 2008
19. M. Kartel, V. Strelko, S. Stavitskaya, V. Mardanenko and L. Kupchik., Combined adsorption
preparations from active carbons, clay minerals and natural plant products., Combined and Hybrid
Adsorbents, NATO Security through Science Series, 2006
20. A. Yablokov, V. Nesterenko, A. Nesterenko, consulting editor Janette D. Sherman-Nevinger.,
Chernobyl. Consequences of the Catastrophe for People and the Environment., Annals of the New
York Academy of Sciences, Volume 1181 4
21. Jungran Yoon, Taeik Ro, Samyol Lee, Shuji Yamamoto and Katsuhei Kobayashi
Measurement of neutron capture cross-section of indium in the energy region from 0.003 eV to 30
keV., Annals of Nuclear Energy V. 29, Issue 10, July 2002
22. Fei Tuo, Fengqun Zhou, Yanling Yi, Xuexiang Cao and Xiangzhong Kong Cross-section
measurements for the reactions of 14 MeV neutrons on indium isotopes., Applied Radiation and
Isotopes V. 64, Issue 8, August 2006
23. J.H. Chao, and A.C. Chiang Activation detection using indium foils for simultaneous
monitoring neutron and photon intensities in a reactor core Radiation Measurements V. 45, Issue 9, October 2010
24. Yu. V. Petrov and A. I. Shlyakhter The cross section of inelastic neutron acceleration for
indium isomers., Nuclear Physics A V. 292, Issues 1-2, November 1977
25. A. Tartaglione, J.J. Blostein and R.E. Mayer Prompt gamma emissions in the reaction 115
In(n,γ) 116In for neutrons around the 1.45 eV absorption resonance., Applied Radiation and Isotopes
V. 67, Issue 9, September 2009
26. F. Tárkányi, A. Hermanne, B. Király, S. Takács, F. Ditrói, M. Baba and A.V. Ignatyuk
Investigation of activation cross sections of deuteron induced reactions on indium up to 40 MeV for
production of a 113Sn/113mIn generator., Applied Radiation and Isotopes V. 69, Issue 1, January 2011
27. T. B. Ryves, J. N. Hunt and J. C. Robertson Neutron capture cross-section measurements for
238U and 115In Between 150 AND 630 keV., Journal of Nuclear Energy V. 27, Issue 8, August 1973
If the roof had fallen in the summer, the radioactive dust would be instantly sold on for miles, but in the current winter weather radioactive dust can threaten only workers NPP, so far ...
The bad news:
Dropped inside the sarcophagus water from melting snow can dramatically increase the radioactivity of the fuel rods:
Water, under the sarcophagus is a source of several kinds of dangers:
- falling on the accumulation of fuel-containing materials, it leads to an increase in the effective neutron multiplication factor in the system;
- water slowly destroys the fuel, and contributes to the uncontrolled movement of radioactivity in the inner rooms and the removal of radionuclides beyond the "Shelter";
- transferring the dissolved salts of enriched uranium, the water can increase the potential danger of a nuclear Object;
- water promotes corrosion destruction of building constructions "Shelter".
- it prevents research to improve the electrical safety of object;
- water violates the normal operation of diagnostic systems. After strong rains have taken place 2 "anomalous" neutron events (significant increase generation of neutrons) recorded by 12 and 16 September 1996. Neutron radiation, which initially increased, after spraying with a solution of gadolinium decreased to usual levels [Official website: Institute of Problems of Safe Development of Nuclear Energy http://www.ibrae.ac.ru/].
Chernobyl experience
Post-Accident Management
Building the Chernobyl "sarcophagus" (object "Shelter") was necessary to reduce emissions of radioactive substances from the fragments 4 reactor. The main reason of problems is the use of temporary structure as permanent [1-2].
Previously in the "clean" area were tested methods of remote connection of large constructions, remote control for concrete pumping equipment, designed a system of television and radio construction control, created special cabins-capsules that allow visually inspect poorly accessible places with the help of cranes. To reducethe overall level of radiation dose was shot and buried radioactive ground, fragments of building constructions and equipment from the area around the reactor, after which the entire area was covered with a layer of gravel and sand thickness of 50 cm and a concrete layer. At this concreting had spent more than 100 000 cubic meters of concrete. [3]
For building of the Chernobyl sarcophagus been used elements of Block 4 destroyed by reactor explosion. This was done to reduce construction period (6 months). But even this variant required the use of more than 200 000 tons of concrete and more than 10 000 tons of steel. The principal disadvantages of this approach are:
- huge collective dose of radiation exposure obtained by builders and fitters;
- necessity to build new structures very close to destroyed reactor in large radiation fields;
- impossibility to fit exactly to each other large metal structures by using remote installation;
- impossibility to assess residual strength of structures after an explosion and fire;
- large masses of concrete were not included in the designated area because of the
imperfections of remote methods of concreting;
- flow of concrete in the damaged areas have limited access to them;
- impossibility accurate and precise work near a strong source of radiation has led to the main
problem of construction - leakage;
- total cracks area was estimated as 1000 square meters. [4-8]
Through the holes every year leaks around 2000 cubic meters of water, which eventually coalesce at rooms of the lower level Block 4. Yearly volumes of condensate at Block 4 is about 1650 cubic meters. The 180 cubic meters/year are the remnants spray for dust suppression. All of this water passes through the debris Block 4 and is going to basement rooms. Every year about 2100 cubic meters of collected water evaporates, and about 1300 cubic meters seeps through the foundation at ground under the Block 4 [9].
Water, under the sarcophagus is a source of several kinds of dangers:
- falling on the accumulation of fuel-containing materials, it leads to an increase in the effective neutron multiplication factor in the system;
- water slowly destroys the fuel, and contributes to the uncontrolled movement of radioactivity in the inner rooms and the removal of radionuclides beyond the "Shelter";
- transferring the dissolved salts of enriched uranium, the water can increase the potential danger of a nuclear Object;
- water promotes corrosion destruction of building constructions "Shelter".
- it prevents research to improve the electrical safety of object;
- water violates the normal operation of diagnostic systems. After strong rains have taken place 2 "anomalous" neutron events (significant increase generation of neutrons) recorded by 12 and 16 September 1996. Neutron radiation, which initially increased, after spraying with a solution of gadolinium decreased to usual levels [2].
Carried out in 1995 - 1997 years studies have shown that the main source of water pollution by 90Sr are oxidised fuel particles U3O8. Their rate of dissolution is much higher than that of the fuel particles UO2.
In the first moments of the accident takes place the destruction of the fuel tablets of uranium dioxide on grain boundaries. During the Chernobyl accident was found that the over time takes place crushing large particles at a more dangerous form for humans [10-14].
Because of the possibility of the collapse of the "Shelter" and the release of radioactive dust into the environment, under the roof was installed dust suppression system, which periodically spray dust suppression solutions. This system has been in operation since 1990, and during this time it was sprayed over 1000 tons of solutions [15].
After the accident comparable with Chernobyl, finely dispersed solid radioactive substances can penetrate into the constructions at a depth of several cm, and the radioactive water at cement screed, plaster, brick at a depth of 10 cm or more. Repeated treatment of decontamination solutions does not usually lead to lower radiation dose rate to acceptable levels. To reduce the level of radiation, it is necessary to cover the surface by lead.
During the Chernobyl accident, the best medical care was assisted for KGB officers. Techniques of enterosorbtion by zeolite and hemodialysis with activated carbon proved their efficiency for removing of radionuclides from the body. Studies have shown that the amount of radionuclides in the body can be reduced by 3-4 times before they produce significant internal exposure [16-20].
Enough quality, to protect from external radiation and radioactive dust, nowadays have only spacesuits for astronauts. For the work at nuclear power plants are most suitable Hard-shell suits. However, they are very heavy and it is necessary to movement a mobile bigger vehicle for one person.
Among other space-based technology may be useful robot arm for different manipulations.
The most expensive and most universal way to protect and cool the reactor is filling it by Indium (In). Indium's high neutron capture cross section for thermal neutrons makes it suitable for use in control rods for nuclear reactors, typically in an alloy containing 80% Silver, 15% Indium, and 5% Cadmium [21-27] In the reactor, together with the indium, need to place thermoelectric elements (based on the Peltier effect) as a coolers. All other variants of cooling require mass transfer of cooling fluid. Radioactive water at the reactor is best to use for the concreting of the internal spaces. In the absence of information about the location of molten uranium fuel, it is better in the water and concrete solutions add boron compounds (B4C for example).
For fast cutting armature rubble, and welding sections of new constructions is best to use plasma torches. Cracks will be formed in construction in any case. The main task is the localization of cracks. In laminated structures, cracks increase mostly within the layer. It must be a sufficient viscosity of the material to resist earthquakes and radiation embrittlement. Lead is consistent most of the requirements. Supporting function should be assigned on the welded, not removable formwork of stainless steel. All other options require additional corrosion protection, which near the source of radiation is difficult to make. The design should be formed layer by layer of lead and concrete. To prevent the formation and movement of radioactive dust by wind, all external surfaces of buildings must be made of steel. Protective structures of steel and concrete, lead, will have considerable weight, and therefore need more support construction for the roof. Temporarily this function can perform reliably fixed crane. On the crane line, fixing the building, must be mounted dampers for the localization of vibrations during earthquakes. It is necessary to mount geodetic marks which allow to determine the sediment and deformation structures in time. For the isolation of radioactive groundwater is necessary under the base lay several layers of rubber. This is usually made by an underground cutter with large number water cutting nozzles. However, all existing models of such units are small in size and are designed for small depth (few meters). To create the underground layers of rubber or heat-resistant materials under nuclear power plants need to design an exclusive technology.
References
1. USSR State Committee on the Utilisation of Atomic Energy "The Accident at the Chernobyl
NPP and its Consequences" IAEA Post Accident Review Meeting, Vienna, 25-29 August 1986.
2. Official website: Institute of Problems of Safe Development of Nuclear Energy
http://www.ibrae.ac.ru/
3. A.R.Sich. “Chernobyl Accident Management Actions”, Nuclear Safety, Vol.35, N1, Janusry-
June 1994
4. "Policy Statement on Regulation of Nuclear and Radiation Safety of"Shelter "on Chernobyl
nuclear power plant. Approved by the Ministerial Order of 08.04.1998, № 49
5. "Analysis of the current safety of the Shelter and forecasts of the situation. " Ans. Artist
Borovoy A.A. Report of ISTC "Shelter ", arch. № 3836
6. Borovoy A.A., Bogatov S.A., Pazukhin E.M. "The current state of the Shelter and its impact on
the environment" / Radiochemistry. - T.41, № 4, 1999
7. Borovoy A.A., Evstratenko A.S., Krinitsyn A.P. et al "Dynamics of the radiation situation at
the"Shelter" object": - 10 years, the main results of scientific research / National Academy of
Sciences of Ukraine. - Chernobyl, 1996
8. Borovoy A.A., Gorbachev B.I., Evstratenko A.S. et al. "aerosol pollution of the Shelter and
submicron aerosols. Collection " Problems of Chernobyl / ISTC NAS. Issue 15. Chernobyl 2004
9. ENVIRONMENTAL IMPACT ASSESSMENT, New Safe Confinement Conceptual Design:
Chernobyl Nuclear Power Plant – Unit 4. State Specialised Enterprise Chernobyl Nuclear Power
Plant, Kiev 2003
10. Bar'yakhtar V.G. Biiky A.A. Borovoy A.A., Karasev B.C. Sarcophagus of today and tomorrow
Kiev, 1992. - S. 1 - 19. - Preprint, Ukrainian Academy of Sciences.
11. Description of the "Shelter" and requirements for its transformation: Report IAE them. IV
Kurchatov Complex expedition; VNIPIET. - Chernobyl, 1991
12. Dushin V.N., Petrov, B.F., Pleskachevsky L.A., and G.S. Boykov, Evdokimov I.V., Korostin
I.Y., Naydenov E.G., Prusakov A.G., Sokolov A.M., Ibraimov G.D., Checherov K.P. "Localization of
sources of intense gamma rays and evaluation of fuel in the Central Hall of the 4-th unit of Chernobyl.
" NPO "Radium Institute ", Inv. № 1732 and, Chernobyl in 1992
13. Usatyj A.F. Generalized results of determination of distributions of major gamma radiation
sources in the central hall of the Sarcophagus, recorded by dosimetric cords using EPR sensors. In:
“Sarcophagus Safety’94”. The State of Chernobyl Nuclear Power Plant Unit 4. Proceedings of an
International Symposium. Zeleney Mys, Ukraine, 14-18 March 1994
14. Borovoi А.А. Analytical Report ( Post- Accident Management of Destroyed Fuel from
Chernobyl ) //IAEA, Work Material, 1990
15. Borovoi А.А., Object "Shelter" Safety Analysis Report 2001
16. Official website: Security Service of Ukraine (In 1986 Ukrainian Department KGB USSR)
http://www.sbu.gov.ua/sbu/control/uk/publish/article?art_id=48991
17. S.V. Mikhalovsky and V.G. Nikolaev Interface Science and Technology., Activated Carbon
Surfaces in Environmental Remediation: Chapter 11 Activated carbons as medical adsorbents V. 7, 2006
18. Patrick J. Faustino et. al. Quantitative determination of cesium binding to ferric
hexacyanoferrate: Prussian blue., Journal of Pharmaceutical and Biomedical Analysis V. 47, Issue 1., 2008
19. M. Kartel, V. Strelko, S. Stavitskaya, V. Mardanenko and L. Kupchik., Combined adsorption
preparations from active carbons, clay minerals and natural plant products., Combined and Hybrid
Adsorbents, NATO Security through Science Series, 2006
20. A. Yablokov, V. Nesterenko, A. Nesterenko, consulting editor Janette D. Sherman-Nevinger.,
Chernobyl. Consequences of the Catastrophe for People and the Environment., Annals of the New
York Academy of Sciences, Volume 1181 4
21. Jungran Yoon, Taeik Ro, Samyol Lee, Shuji Yamamoto and Katsuhei Kobayashi
Measurement of neutron capture cross-section of indium in the energy region from 0.003 eV to 30
keV., Annals of Nuclear Energy V. 29, Issue 10, July 2002
22. Fei Tuo, Fengqun Zhou, Yanling Yi, Xuexiang Cao and Xiangzhong Kong Cross-section
measurements for the reactions of 14 MeV neutrons on indium isotopes., Applied Radiation and
Isotopes V. 64, Issue 8, August 2006
23. J.H. Chao, and A.C. Chiang Activation detection using indium foils for simultaneous
monitoring neutron and photon intensities in a reactor core Radiation Measurements V. 45, Issue 9, October 2010
24. Yu. V. Petrov and A. I. Shlyakhter The cross section of inelastic neutron acceleration for
indium isomers., Nuclear Physics A V. 292, Issues 1-2, November 1977
25. A. Tartaglione, J.J. Blostein and R.E. Mayer Prompt gamma emissions in the reaction 115
In(n,γ) 116In for neutrons around the 1.45 eV absorption resonance., Applied Radiation and Isotopes
V. 67, Issue 9, September 2009
26. F. Tárkányi, A. Hermanne, B. Király, S. Takács, F. Ditrói, M. Baba and A.V. Ignatyuk
Investigation of activation cross sections of deuteron induced reactions on indium up to 40 MeV for
production of a 113Sn/113mIn generator., Applied Radiation and Isotopes V. 69, Issue 1, January 2011
27. T. B. Ryves, J. N. Hunt and J. C. Robertson Neutron capture cross-section measurements for
238U and 115In Between 150 AND 630 keV., Journal of Nuclear Energy V. 27, Issue 8, August 1973