46th annual hps mtg; mpm-b.31 two sample preparation methods for measuring 3 h and 14 c in...
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46th Annual HPS Mtg; MPM-B.3
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Two Sample Preparation Methods for Measuring 3H and
14C in Incinerator Ash and Spent Lime
Ben Edwards, Le-Xuan Thai and Dan Sprau
Master's Project - East Carolina University
in partial fulfillment of the requirements for the degree of MS in
Occupational Safety
Duke University Medical CenterDivision of Radiation Protection
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Problem:
Analyze two selected methodologies for measuring 3H and 14C in ash and spent lime from the incineration of low level radioactive biomedical research waste.
Assess the analytical performance of each method.
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Relevance
Radioactive material was used in the development of every major drug discovered since 1946, and in millions of analytical, diagnostic, and therapeutic medical procedures each year in the US.
Radioactive waste from this biomedical use is highly regulated. Disposal is expensive, particularly for 3H and 14C. Radioactive waste management dissipates biomedical research institutions' financial resources.
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Relevance (cont’d)
Incineration generates ash and spent lime waste. Disposal of this waste as non-radioactive requires demonstrating that the radioactive concentration does not exceed specified regulatory limits. Disposal of the ash and lime as radioactive waste is prohibitively expensive.
A reliable analytical method, capable of achieving the required sensitivity, can reduce waste disposal costs of academic, industrial and government biomedical research facilities.
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Performance Criteria
Count time t needed, for each nuclide and material, to achieve a specified "minimum detectable concentration" [MDC] based on the regulatory constraints
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MDC Formula
MDC = [2.71+4.65(RBxt)½]x[60xExMxYxt]-1 RB = Background count rate in counts minute-1
(cpm) t = Background & gross count time (minutes) E = Counter efficiency (counts/disintegration) M = Sample mass (g)
60 = disintegrations minute–1 [dpm] per Bq of activity
Y = fraction of chemical yield, if applicable
Gollnick (1994)
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Target MDC
Specified regulatory limits: 37 Bq g-1 for 3H 1.1 Bq g-1 for 14C[10 CFR 20 App. B Table 2 Column 2; PG 8-10 (1997)]
Per Fong and Alvarez (1997), set target MDC at 1/10 of regulatory limit; target MDC:
3.7 Bq g-1 for 3H 0.11 Bq g-1 for 14C
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Specific Activity [C] Formula
C = (S - RB)Y (E M)-1
S = sample [gross] count rate (cpm)
RB = Background count rate (cpm)
Y = sample yield E = counting efficiency (dpm/cpm) M = sample mass (g)
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Available Methods
Oxidation - combustion of the solid sample in an oxygen-rich environment; drives off the 3H as HTO vapor and the 14C as 14CO2. These gaseous combustion products are then captured in separate collection vials for liquid scintillation counting.
Gel Suspension - the powdered solid sample material is suspended in a gel-forming liquid scintillation counting solution.
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Measurement Results
3H (Bq g-1) 14C (Bq g-1)
Material/Method
Mean Std. Dev.
Mean Std. Dev.
Ash/Oxidizer 32.4 13.3 0.74 0.47
Ash/Gel 0.6 0.3 0.80 0.07
Lime/Oxidizer 13.3 0.7 0.24 0.04
Lime/Gel 8.1 0.5 0.57 0.07
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Time to Achieve MDC
3H Count Timea
(minutes) 14C Count Timeb
(minutes)
Ash/Oxidizer < 1 79
Ash/Gel 22 7559Lime/Oxidizer
<1 77
Lime/Gel 22 1175a 3H MDC = 3.7 Bq g-1
b 14C MDC = 0.11 Bq g-1
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Conclusions
Both methods easily achieve 3H MDC
Only oxidizer achieves 14C MDC in less than 2 hours; gel takes 126 hours for ash & 26 hours for lime
Gel method fails to detect 95+% of 3H in ash
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Sampling Campaign
(n=30)
Nuclide
Material
Method Sample
(g)
Count t(minutes)
3H Ash Oxidation
0.5 20
14C Ash Oxidation
0.5 180
3H Lime Oxidation
0.5 20
14C Lime Oxidation
0.5 180
3H Ash Gel 0.1 18014C Ash Gel 0.1 1803H Lime Gel 0.1 18014C Lime Gel 0.1 180
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0.0
5.0
10.0
15.0
20.0
25.0
0 5 10 15 20 25 30 35
Ox-Ash
Ox-LimeGel-Ash
Gel-Lime
3H MDC vs count time
Count time (minutes)
Desired MDC
(3.7 Bq g-1)
MDC(Bq g-
1)
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14C MDC vs count time
0.00.20.40.60.81.01.21.41.61.82.0
0 1000 2000 3000 4000
Ox-Ash
Ox-Lime
Gel-Ash
Gel-Lime
MDC(Bq g-1)
Desired MDC
(0.11 Bq g-1)
Count time (minutes)
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Error Propagation
If x, y, z, … are directly measured variables
for which we know the standard
deviations x, y, z,…, then the standard
deviation for any quantity u derived from
these counts can be calculated from:
u² = (u/x)²x² + (u/y)²y² + (u/z)²z² + …where u = u(x, y, z, …) is the derived quantity.
Knoll (1989)