Technetium-99

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Technetium-99, 99Tc
General
Decay mode
Decay energy (MeV)
Beta decay0.2975
Isotopes of technetium
Complete table of nuclides

Technetium-99 (99Tc) is an isotope of

thermal neutron fission of uranium-235
.

The metastable

isomeric transition
to technetium-99, a desirable characteristic, since the very long half-life and type of decay of technetium-99 imposes little further radiation burden on the body.

Radiation

The weak beta emission is stopped by the walls of laboratory glassware. Soft X-rays are emitted when the beta particles are stopped, but as long as the body is kept more than 30 cm away these should pose no problem. The primary hazard when working with technetium is inhalation of dust; such radioactive contamination in the lungs can pose a significant cancer risk.[citation needed]

Role in nuclear waste

Yield, % per fission[1]
Thermal
Fast
14 MeV
232Th not fissile 2.919 ± .076 1.953 ± 0.098
233U 5.03 ± 0.14 4.85 ± 0.17 3.87 ± 0.22
235U 6.132 ± 0.092 5.80 ± 0.13 5.02 ± 0.13
238U not fissile 6.181 ± 0.099 5.737 ± 0.040
239Pu 6.185 ± 0.056 5.82 ± 0.13 ?
241Pu 5.61 ± 0.25 4.1 ± 2.3 ?

Due to its high fission yield, relatively long half-life, and mobility in the environment, technetium-99 is one of the more significant components of nuclear waste. Measured in becquerels per amount of spent fuel, it is the dominant producer of radiation in the period from about 104 to 106 years after the creation of the nuclear waste.

samarium-151 with a half-life of 90 years, though a number of actinides produced by neutron capture
have half-lives in the intermediate range.

Releases

Long-lived fission products
Nuclide
t1⁄2
 Yield Q[a 1]
βγ
(
Ma
) 		(%)[a 2] (
keV
)
99Tc 0.211 6.1385 294 β
126Sn
 0.230 0.1084 4050[a 3] βγ
79Se 0.327 0.0447 151 β
135Cs
 1.33  6.9110[a 4] 269 β
93Zr
 1.53  5.4575 91 βγ
107Pd
 6.5   1.2499 33 β
129I 15.7   0.8410 194 βγ
  1. ^ Decay energy is split among β, neutrino, and γ if any.
  2. ^ Per 65 thermal neutron fissions of 235U and 35 of 239Pu.
  3. ^ Has decay energy 380 keV, but its decay product 126Sb has decay energy 3.67 MeV.
  4. ^ Lower in thermal reactors because 135Xe, its predecessor, readily absorbs neutrons.

An estimated 160

nuclear fuel reprocessing; most of this was discharged into the sea. In recent years, reprocessing methods have improved to reduce emissions, but as of 2005 the primary release of technetium-99 into the environment is by the Sellafield plant, which released an estimated 550 TBq (about 900 kg) from 1995–1999 into the Irish Sea. From 2000 onwards the amount has been limited by regulation to 90 TBq (about 140 kg) per year.[3]

In the environment

The long half-life of technetium-99 and its ability to form an

134Cs) and strontium (e.g., 90Sr). Hence the pertechnetate escapes through these treatment processes. Current disposal options favor burial in geologically stable rock. The primary danger with such a course is that the waste is likely to come into contact with water, which could leach radioactive contamination into the environment. The natural cation-exchange capacity of soils tends to immobilize plutonium, uranium, and caesium cations. However, the anion-exchange capacity is usually much smaller, so minerals are less likely to adsorb the pertechnetate and iodide
anions, leaving them mobile in the soil. For this reason, the environmental chemistry of technetium is an active area of research.

Separation of technetium-99

Several methods have been proposed for technetium-99 separation including: crystallization,[4][5] liquid-liquid extraction,[6][7][8] molecular recognition methods,[9] volatilization, and others.

In 2012 the crystalline compound Notre Dame Thorium Borate-1 (NDTB-1) was presented by researchers at the University of Notre Dame. It can be tailored to safely absorb radioactive ions from nuclear waste streams. Once captured, the radioactive ions can then be exchanged for higher-charged species of a similar size, recycling the material for re-use. Lab results using the NDTB-1 crystals removed approximately 96 percent of technetium-99.[10][11]

Transmutation of technetium to stable ruthenium-100

An alternative disposal method, transmutation, has been demonstrated at CERN for technetium-99. This transmutation process bombards the technetium (99
Tc as a metal target) with neutrons, forming the short-lived 100
Tc (half-life 16 seconds) which decays by beta decay to stable ruthenium (100
Ru). Given the relatively high market value of Ruthenium[12] and the particularly undesirable properties of Technetium, this type of nuclear transmutation appears particularly promising.

See also

References

  1. IAEA
    . Retrieved 18 December 2020.
  2. ^ a b K. Yoshihara, "Technetium in the Environment" in "Topics in Current Chemistry: Technetium and Rhenium", vol. 176, K. Yoshihara and T. Omori (eds.), Springer-Verlag, Berlin Heidelberg, 1996.
  3. ISSN 1345-4749
    .
  4. ISSN 0020-1669
    .
  5. PMC 9916763
    .
  6. ISSN 1588-2780
    .
  7. ISSN 0236-5731
    .
  8. doi:10.1016/j.talanta.2018.03.034
    .
  9. ISSN 1588-2780
    .
  10. ^ William G. Gilroy (Mar 20, 2012). "New Method for Cleaning Up Nuclear Waste". Science Daily.
  11. S2CID 96158262
    .
  12. ^ "Daily Metal Price: Ruthenium Price Chart (USD / Kilogram) for the Last 2 years".
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