1 / 16

Two Sample Preparation Methods for Measuring 3 H and 14 C in Incinerator Ash and Spent Lime

Duke University Medical Center Division of Radiation Protection. Two Sample Preparation Methods for Measuring 3 H and 14 C in Incinerator Ash and Spent Lime. Ben Edwards , Le-Xuan Thai and Dan Sprau Master's Project - East Carolina University

arawn
Download Presentation

Two Sample Preparation Methods for Measuring 3 H and 14 C in Incinerator Ash and Spent Lime

An Image/Link below is provided (as is) to download presentation Download Policy: Content on the Website is provided to you AS IS for your information and personal use and may not be sold / licensed / shared on other websites without getting consent from its author. Content is provided to you AS IS for your information and personal use only. Download presentation by click this link. While downloading, if for some reason you are not able to download a presentation, the publisher may have deleted the file from their server. During download, if you can't get a presentation, the file might be deleted by the publisher.

E N D

Presentation Transcript


  1. Duke University Medical Center Division of Radiation Protection 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 46th Annual HPS Mtg; MPM-B.3

  2. 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. 46th Annual HPS Mtg; MPM-B.3

  3. 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. 46th Annual HPS Mtg; MPM-B.3

  4. 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. 46th Annual HPS Mtg; MPM-B.3

  5. Performance Criteria • Count time t needed, for each nuclide and material, to achieve a specified "minimum detectable concentration" [MDC] based on the regulatory constraints 46th Annual HPS Mtg; MPM-B.3

  6. 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) 46th Annual HPS Mtg; MPM-B.3

  7. Target MDC Specified regulatory limits: • 37 Bq g-1for 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-1for 3H • 0.11 Bq g-1 for 14C 46th Annual HPS Mtg; MPM-B.3

  8. 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) 46th Annual HPS Mtg; MPM-B.3

  9. 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. 46th Annual HPS Mtg; MPM-B.3

  10. Measurement Results 46th Annual HPS Mtg; MPM-B.3

  11. Time to Achieve MDC a 3H MDC = 3.7 Bq g-1 b 14C MDC = 0.11 Bq g-1 46th Annual HPS Mtg; MPM-B.3

  12. 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 46th Annual HPS Mtg; MPM-B.3

  13. Sampling Campaign (n=30) 46th Annual HPS Mtg; MPM-B.3

  14. 3H MDC vs count time MDC (Bq g-1) Desired MDC (3.7 Bq g-1) Count time (minutes) 46th Annual HPS Mtg; MPM-B.3

  15. 14C MDC vs count time MDC (Bq g-1) Desired MDC (0.11 Bq g-1) Count time (minutes) 46th Annual HPS Mtg; MPM-B.3

  16. 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)²x² + (u/y)²y² + (u/z)²z² + … where u = u(x, y, z, …) is the derived quantity. Knoll (1989) 46th Annual HPS Mtg; MPM-B.3

More Related