Post on 08-Feb-2016
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Radiation Reactions: Dosimetry and Hot Atom Chemistry
• Dosimetry• Radiation Protection• Hot Atom Chemistry
Radicals are formed by the interaction of radiation with water
Radicals drive reactions
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Radiation Dosimetry• Units• Measurements• Neutrons and charged particles• LET• Dose Calculations
Dosimetry• Quantitative relation between specific measurement in a
radiation field and chemical and/or biological changes§ dose effect relationship§ caused by production of ionized molecules, atoms,
secondary electrons§ chemical changes, biological effects
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Units• Exposure
§ defined as amount of ionization in air caused by g and x-rays
§ roentgen (R) defined as amount of g or x-rays that produced 1 esu of charge in 1 mL of air at STP (1.293E-3 g)
§ new definition includes primary and secondary ionization
§ ∆Q/∆m; ∆Q charges of one sign, ∆m mass of airrefers only to EM radiation in air1 R = 2.58x10-4 C/kg
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Dose Units• Absorbed Dose
§ energy absorbed per unit mass of target for any kind of ionizing energy
§ Gray (Gy) = 1J/kg§ in US; rad = 100 erg/g§ 1J/kg = 107 erg/103 g = 104 erg/g = 102 rad
• Absorbed dose is referred to as dose• Treated as point function, having a value at every position
in an irradiated object1 eV = 1.60E-19 J1 charge pair separation =1.60E-19 C1R = 2.58E-4 C/kg x 34 J/C = 8.8E-3 Gy
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Dose Equivalent• Absorbed dose needed to achieve biological effect is
different for different types of radiation§ Difference due to high versus low LET§ Dose equivalent compensates for this difference§ H (dose equivalent) = QD§ Q is dimensionless, has some different values§ Q=fn(particle, energy); 1≤Q≤20
à Q from NCRP Report 116§ uses LET (L) in keV/µm in water
• In soft tissue 1R produces 9.5E-3 Gy§ called rep (roentgen-equivalent-physical) no longer
used
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Dose Equivalent
• When dose in Gy, dose equivalent is Sv• When dose in rad, dose equivalent is rem (roentgen-
equivalent-man)• 1 Gy = 100 rad, 1 Sv = 100 rem• Particle type and energy should be explicitly considered• Distribution in tissue depends on isotope
§ I goes to thyroid§ Sr, Ra go to bone§ Cs, H go all over§ Metals go towards liver § Complexes can be released in kidneys
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QF Values for Various Types of RadiationRadiation QFX and grays 1Electrons and Positrons 1Neutrons, E < 10 keV 3Neutrons, E > 10 keV 10Protons 1-10Alpha Particles 1-20Heavy Ions 20
Q Dependence on LETLET (L) Q(kev/µm in water)<10 110-100 0.32L-2.2>100 300/L^0.5
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Calculations• Alpha and Beta• Absorbed dose: D = AEavex1.6E-13J/MeVx1E3g/kg
=1.6E-10AEave (Gy/s)A = conc. Bq/g, Eave= average energy
Calculated dose of 1.2 E5 Bq of 14C in 50g of tissueßmax of 14C is 0.156 MeVEave≈ ßmax/3 ≈ 0.052 MeVA = 1.2 E5 Bq/50gD = 1.2 E5 Bq/50g x 0.052 MeV x 1.6E-10 = 20 nGy/s
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More Dose Calculations• Photons• µ/r is air energy absorption coefficient= 0.0027 m2/kg for 60 keV to 2 MeVD = 3.44E-17 CE/r2 (Gy/s)C in Bq, E in MeV and r, distance from source, in mgamma energy needs to normalized to %Dose from 10000 Bq 38S at 0.1 m95 % 1.88 MeV = 1.786 MeVD= 3.44E-17 x 1E5 x 1.786 / 0.12
D = 6.14E-10 Gy/sNeed to consider average gamma energy
DCE
4r2
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Biological Effects
Time Event10-18 seconds Absorption of Ionizing Radiation10-16 seconds Ionization, Excitation10-12 seconds Radical formation, bond breakage10-12 to 10-6 seconds Radical reactionMin. to Hrs. Cellular ProcessesHrs. to Months Tissue DamageYears Clinical effectsGenerations Genetic Effects
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Biological Effects Concepts
• Linear Effect of Dose§ Based on Atomic Bomb survivor data§ Mandated by law
à Any amount radiation above background is harmful
§ Low level radiation effect not so clearà No real evidence of health effects from any
amount above backgroundà Some evidence of positive health effects with
small increase in radiation§ Recent efforts in low dose research
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Radiation Protection• 3.6 mSv/y Typical background radiation to US public(≈ 80% from natural sources)• 2.4 mSv/y Average dose to US nuclear industry employees.
(0.01mSv/y to public)• 350 mSv in lifetime Criterion for relocating people after
Chernobyl• 50 mSv annual worker dose limit• 15 µSv to public from TMI in 50 mile radius• 0.4 mSv from dental x-rays• 1000 mSv as short term dose: causes (temporary) radiation
sickness.• 5000 mSv as short term dose: would kill about half those
receiving it within a month.• 10,000 mSv as short term dose: fatal within days
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Regulations (US)• Dose limits vary from country to country• Directed towards occupational exposure
§ Public limits generally 10%• Rules set up by NRC (10CFR76.60) based on Atomic
Energy Act of 1954§ http://www.nrc.gov/reading-rm/doc-collections/cfr/
part020/à sets limits for isotopes, total exposure, procedures
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US Regulations
• Annual occupational limits§ 50 mSv total effective dose§ 0.5 Sv to any individual tissue or
organ(except eye)§ 0.15 Sv to eye§ 0.50 Sv to skin or to each extremity§ U intake limited to 10 mg/week
à Details at http://www.nrc.gov/reading-rm/doc-collections/cfr/part020/part020-1201.html
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More regulationsDose to Public
• Total dose 1 mSv/year• not exceed 0.02 mSv in any one hour• may apply for 5 mSv/y• Compliance shown by 0.02 mSv in any one hour
or 0.5 mSv/y in uncontrolled area• For a nuclear waste repository 0.25 mSv/y• A risk of a detriment is associated with dose• Does not calculate number of people
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Probability Coefficients for Stochastic Effects
Detriment Adult Workers Whole Pop.(1E-2/Sv) (1E-2/Sv)
Fatal Cancer 4.0 5.0Nonfatal Cancer 0.8 1.0Severe geneticeffects 0.8 1.3
TOTAL 5.6 7.3
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Calculations
What is probability of detriment from 2 mSv/y for 10 years to adult worker?
2E-3 Sv/y x 5.6E-2/Sv x 10 y = 1.1E-3From maximum occupation dose for 30 years50E-3 Sv/y x 5.6E-2/Sv x 30 y = 0.084
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Intake limits• Air and water
§ nuclide specific (include daughter)§ Class refers to lung retention (Days, Weeks, Years)§ Annual limits on Intake (ALI) derived from 0.05
Sv total dose or 0.5 Sv dose to an organ or tissue§ Derived air concentration (DAC) comes from ALIDAC = ALI/(2000 hr x 60 min/hr x 2E4 mL/min)
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Intake Limits
§ Public limited based on 0.5 mSv dose if concentrations continuously ingested or inhaled
Ingestion of 7.3E7 mL/y• Sewer Disposal
§ Based on sewer water only water source, 5 mSv total dose per year
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Americium-241
AtomicNo.
Radio-nuclide Class
Table 1Occupational Values
Table 2Effluent
Concentrations
Table 3Releases
toSewersCol. 1 Col. 2 Col.
3Col. 1 Col. 2
OralIngestion
ALI(µCi)
Inhalation
Air(µCi/ml)
Water(µCi/ml)
MonthlyAverage
Concentration(µCi/ml)
ALI(µCi)
DAC(µCi/ml)
95 Am-241 W, all compounds
8E-1Bone Surf
6E-3Bone Surf
3E-12
- - -
(1E+0) (1E-2) - 2E-14 2E-8 2E-7
Isotope data found at: http://www.nrc.gov/reading-rm/doc-collections/cfr/part020/appb/
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Hot Atom Chemistry• Chemical reactions produced by nuclear transformation
§ Neutron irradiation of ethyl iodideà Iodine extracted into aqueous phase
* 127I(n,g)128IË Possible to produce specific isotope
• Conditions needed§ Bond of produced atom must be broken § Should not recombine with fragments§ Should not exchange with target molecule
à Slow kinetics § Separation of new species
• Bonds are broken due to reaction energy§ Bond energies on the order of eV§ In neutron capture the emitted photon provides recoil
• Halogens produced in this method
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Hot Atom Chemistry• Beta reactions
§ TeO32-IO3
- + e-
à Recoil is not quantized* Kinetic energy shared* E is maximum beta energy (MeV)
Ë Rmax(eV)=573E(E+1.02)/MË 0.5 MeV in 100 amu is about 4 MeV
* Energy is distributed Ë Translational, rotational, vibrational
* Bond usually not broken§ Internal conversion set atom in excited state
à Rearrangement of electrons
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Hot Atom Chemistry
• Conservation of momentum imparts recoil§ Solve based on momentum§ For M in amu and E photon
energy in MeVà Er(eV)=537E2/M
§ Photon on the order of 7 MeV
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Review
• Dosimetry§ Calculations§ Units§ limitation § Influence of particles§ Measurements
• Hot Atom Chemistry§ Energetic processes
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Questions
• Compare DAC for isotopes of Pu and Cs• Perform a dose calculation for 1 mg internal
exposure of 210Po• Use DAC to evaluate experimental limits for
241Am• Calculate the dose from 500000 Bq of 241Am at
0.050 m• What are the principles of hot atom chemistry