Alpha Attenuation Due to Dust Loading. Amber E. Dailey Francis Marion University Savannah River Site

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Transcription:

Alpha Attenuation Due to Dust Loading Amber E. Dailey Francis Marion University Savannah River Site

Purpose The purpose of this experiment was to properly correct for the attenuation of the energy of alpha particles due to dust loading on glass fiber filters used for air monitoring in facilities

Why alpha particles? Alpha particles were the radiation type of interest in this study because they are the most easily attenuated radioactive emission they can be completely stopped by something as thin as a sheet of paper Air can also have a stopping effect on alpha particles this is our concern

What s s so special about air filters? These air filters are used to monitor the amount of airborne radioactivity in a specific area This monitored amount is used, along with other factors, to estimate a personnel radiation dose to the lungs

So, how does it work? These air filters are allowed to run for different sampling times at different facilities Once the sampling time is up, the filters are processed (ran through a radiation counter) and any showing a higher than normal activity are pulled for further inspection If it is found that the higher than normal activity is truly present, the personnel working in that area during the sampling time may need to go on a monitoring program to be sure that they have not received a problematic exposure

Why is this important? Normally, the alpha dose the is counted is corrected by 20% in order to correct for possible attenuation this correction factor may not be accurate in all cases Previous studies (Luetzelschwab and Higby) have shown that dust loading may cause a counting loss by as much as: 28% for samples collected weekly 40% for samples counted bi-weekly There has not yet been a study with sufficient results to properly correct for attenuation due to dust loading on the filters Although, Prior work [Broome 2005] indicated significant decreases in alpha count rate (as much as 38%) due to dust loading, especially on filters from facilities where sampling takes place over long intervals

What was my purpose? My purpose was to see how much dust could, hypothetically, cover the surface of the filter containing the alpha particles before more than 20% of the particles were being attenuated After this point of dust covering, the 20% correction factor will not cut it for an accurate representation of dose

Materials Used The three detectors used in this experiment were: Canberra Series 5 low background gas proportional counter Dual phosphor Eberline HandECount portable scaler Ortec vacuum chamber with Canberra PIPS detector These detectors were chosen because they are the main detectors used for counting air filter samples

Materials Used An attenuator set composed of 9 attenuators of varying density thicknesses of Mylar ranging from 0.41mg/cm 2 to 3.51mg/cm 2 used to simulate a dust covering A 47mm 0.031µCi NIST traceable Americium-241 source

Canberra Series 5 Detector Contains gas-flow proportional and guard detector that both use P-10 gas Low background alpha/beta counter with beta background as low as 0.5 cpm 4 inches of lead shielding 2.25 inch detector Detector window density thickness is 80 µg/cm 2 Sample lies 8.92mm from detector

Canberra Series 5 Detector detector 8.92mm source

Canberra Series 5 Detector

Eberline Hand E Count 2 dual phosphor scintillation counter Alpha efficiency 90% Beta efficiency 25% to 35% Efficiency calculated as: Background <=3cpm alpha and <=60cpm beta Source lies 4.2mm from scintillator

Eberline HandECount detector scintillator 12.7mm air source 4.2mm.97mm

Eberline HandECount PDA for data display Detector housing Drawer containing sample

Eberline Hand E Count Connecting Cable Detector assembly Modular Detector Board Scintillator 50.91 mm 12.75 mm

Alpha Spectrometer Composed of EG&G Ortec 808 vacuum chamber and Canberra PIPS Detector Chamber is evacuated using Welch Series W vacuum pump PIPS Detector fabricated using photolithographic techniques Face of detector is ion-implanted Detector operates at 40V Background count rate <0.05 counts/hr/cm 2 Window thickness <2µm Sample lies 12.17mm below bottom of detector

Alpha Spectrometer PIPS detector 16mm 12.17mm source height-adjustable shelf 0.97mm alpha spectr oscopy chamber

Alpha Spectrometer

The Attenuator Set Attenuators were built using cards with dimensions equal to the dimensions of the cards that surround the glass fiber filters being investigated A 2.25 hole (slightly larger than diameter of glass fiber filters) was punched in the card Cards were then adhered to layers of Mylar of varying density thicknesses

Attenuator Set

Appearance of Attenuator

Attenuator Card Filter Card

Method Background counts were obtained and recorded for each detector used everyday The Americium-241 source was counted for either 30 minutes or duration sufficient to acquire 10,000 counts, whichever took less time The count was done ten times per density thickness attenuator

Method A percent deviation of no more than 6% was the data standard to ensure accuracy of counts The multiple counts were first taken when the source was uncovered and successively for each density thickness of Mylar covering Data was analyzed and alpha absorption curves were produced for each detector by plotting the count rate (in cpm) vs. the density thickness of the attenuating material (in mg/cm 2 )

Canberra 5 Results 20% attenuation takes place between 0.82 and 1.37mg/cm 2 80% attenuation takes place between 2.33 and 2.74mg/cm 2 Count Rate vs. Density Thickness Canberra 5 20000 18000 16000 Count Rate (cpm) 14000 12000 10000 8000 6000 4000 2000 0 0 0.5 1 1.5 2 2.5 3 3.5 Density Thickness (mg/cm^2)

Canberra 5 Results Alpha and Beta Counts Alpha Betas 20000 18000 16000 Count Rate (CPM) 14000 12000 10000 8000 6000 4000 2000 0 0 0.5 1 1.5 2 2.5 3 3.5 Density Thickness (mg/cm^2)

HandECount Results 20% attenuation takes place between 0.82 and 1.37mg/cm 2 80% attenuation takes place between 2.33 and 2.74mg/cm 2 Count Rate vs. Density Thickness HandECount 25000 20000 Count Rate (cpm) 15000 10000 5000 0 0 0.5 1 1.5 2 2.5 3 3.5 Density Thickness (mg/cm^2)

HandECount Results Beta counts increase as Alpha counts decrease 25000 Alpha and Beta Counts Alpha Beta 20000 Count Rate (CPM) 15000 10000 5000 0 0 0.5 1 1.5 2 2.5 3 3.5 Density Thickness (mg/cm^2)

Alpha Spectrometer Results 20% attenuation takes place between 1.78 and 2.33mg/cm 2 80% attenuation takes place between 2.33 and 2.74mg/cm 2 Count Rate vs. Density Thickness PIPS 16000 14000 12000 Count Rate (cpm) 10000 8000 6000 4000 2000 0 0 0.5 1 1.5 2 2.5 3 3.5 Density Thickness (mg/cm^2)

Alpha Spectrometer Results 0 attenuation Actual Americum-241 peak occurs at 5486keV 1.37mg/cm 2 attenuation 3.51mg/cm 2 attenuation Energy line at 5485.6keV Energy line at 4341keV Energy line at 1605keV *Resolution is greatly decreased

Results 25000 Count Rate vs. Density Thickness Canberra PIPS HandECount 20000 Count Rate(cpm) 15000 10000 5000 0 0 0.5 1 1.5 2 2.5 3 3.5 density thickness(mg/cm^2)

Results Counts without attenuation are varied due to the distance from the source to the detector These distances are 4.2, 8.92 and 12.17mm As expected, the number of counts is inversely proportional to the distance between source and detector This is due to the range of an alpha in air, given by: R a = 1.24E 2.62 where: E is alpha particle energy in MeV R a is the range of the alpha particle in cm

Future Studies Facilities will perform dust loading studies in order to determine the proper sampling periods, so that it will be unlikely that there will be attenuation greater than is corrected for.

References Higby, D.P. Effects of Particle Size and Velocity on Burial Depth of Airborne Particles in Glass Fiber Filters, PNL- 5278, Pacific Northwest Laboratory, Richland, WA, 1984. Luetzelschwab, J.W., C. Storey, K. Zraly, and D. Dussinger, Self Absorption of Alpha and Beta Particles in a Fiberglass Filter, Health Physics, 79:425-430; 2000. Broome, M.A. Defense Waste Processing Facility (DWPF) Air Sample Dust-Loading Study, CBU-WSP-2005-00065, Savannah River Site, Aiken, SC, 2005. Hadlock, D.J. Workplace Air Monitoring Technical Basis Manual, WSRC-IM-2001-00025, Revision 1, 2005. And a Special Thanks to Ron Smith and Dennis Hadlock!