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15th Annual OSC Readiness Training Program
Sampling Airborne Radioactivity
Generic Soil Sampling
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Air Sampling Primary Tasks
1. Collect
2. Count
3. Calculate
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Air Monitoring Air monitors
Alpha• Isotope specific• Sensitive to dust• Low sensitivity
Beta• Complex• Not Isotope Specific
Gamma• Particulate Size important• Chemistry important
Not a stand alone field instrument because additional analysis is required.
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Purpose of Sampling
Protect workers Normally have respiratory protection Work close to scene, changing radiological
conditions Personal or representative sampling
Protect public No respiratory protection More stable radiological conditions Lower thresholds… larger samples
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Air Sampling Considerations
Sampler power, exhaust, location Filter type Collection time Interferences Atmospheric conditions Labeling Handling Disposition
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Air Sampling Considerations
Airborne alpha radioactivity at 1 DAC that falls out and deposits on flat surfaces may only attain 10% of the criteria for removable contamination.
Alpha contamination in excess of 100 times the criteria for removable contamination may only generate 10% of a DAC when walking through.
CONCLUSION: DACs are not a good indicator of surface contamination, and vice versa; but SHOULD be considered.
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Air Sampler Calibration
Calibrate annually.
Calibration is filter media specific – changing filter type invalidates calibration.
Follow steps in H-810 quick start procedure.
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Air Sampler Calibration
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Collecting Sample(s)
Equipment needed: H-810 air sampler Glass fiber particulate filters Glassine envelope Sharpie Tweezers Generator or AC power
• H-810 sensitive to power quality, check for generator/air sampler compatibility before deploying.
Quick Start Guide for Radeco High Volume Air Sampler -Model H-810
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H-810 Air Sampler
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Safety Precautions
Use GFCI electrical cables/ cords to reduce potential shock hazard.
Be careful of potential static electricity. Do not allow interior of air sampler to get wet
or allow other materials in. Keep electrical cords up off the ground. Securely fasten sampler to tripod or other
working surface. Use hearing protection and eye safety.
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Air Sampling Procedure
Place samplers. Up/down wind, source & receptor site.
Install glass fiber filter, type LB-5211, rough side out, marked with an ‘X’ on the rim of the filter.
Turn on power, 5 – 10 sec warm up.
Press ‘CLEAR’ and then ‘START’ twice.
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Air Sampling Procedure (cont.)
Adjust flow rate (4 cfm suggested).
Press ‘STOP’ and then press ‘CLEAR’ key twice.
Press ‘SET’ key, set total air volume to sample, minimum of 120 ft3 (30 min sample time), longer (8+ hours) is better.
Press ‘ START’ key, sampler will stop when target volume is reached.
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Air Sampling Procedure (cont.)
Record the sample location, start time and flow rate in field logbook.
Sampler will run until target volume has been sampled.
Collect upwind/background air sample in same manner.
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Retrieving Air Sample
Put on Nitrile or similar gloves for contamination control.
Record the ending time and flow volume in the logbook.
Remove filter from the sampler with tweezers and place in glassine envelope.
Record on envelope: sample location, sample number, sample start time, sample volume, sample collection time.
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Retrieving Air Sample
Wipe sampling ring and filter holder with moist paper towel.
Repeat procedure for other samples.
Start second round of sample collection as directed.
Bring air filter media back to command post for counting.
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Counting Samples
Equipment needed: Model 3030 Alpha/Beta sample counter Alpha and Beta QC disc sources
• BPA No. B3-1102-NTLX• Th-230, 1” disc, $425• Sr-90, 2”disc, $425
Nitrile gloves, tweezers, planchets Quick Start Guide for Ludlum Alpha/Beta
Sample Counter - Model 3030
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Ludlum 3030
Alpha/Beta Sample Counter
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Counter QC Procedure
Perform while air samples are being collected .
Plug in system, turn on, press “QC CHECK”. Set count time for 1 minute. Insert alpha calibration source, close/latch
tray, and press “COUNT”. When alpha count is finished, replace alpha
source with beta calibration source, close/latch tray, and press “COUNT”.
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Counter QC Procedure
When beta count is finished, remove source, insert clean planchet, close/latch tray, and press “COUNT” - a background count is performed.
When background count is finished, the QC light should go out, instrument is ready for sample counting.
If QC light does not go out, conduct QC check again and/or check operating parameters.
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Counting Samples
1. Allow sample to decay for 3 hours
0
500
1000
1500
2000
2500
3000
3500
4000
4500
0 30 60 90 120 150 180 210 240 270
Time (min)
Cou
nts Alpha
Beta
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Counting Samples
Select count time, longer count time leads to lower MDA, 3030 software provides MDA estimate.
Place background sample on planchet, position on sample tray, close/latch tray. Apply contamination control techniques.
Press the “COUNT” key and adjust volume to desired level.
Colon symbol on the display indicate the count is in process.
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Counting Samples
CPM or DPM. Establish during Model 3030 set up.
Record time of sample count and alpha-beta count data, note units (CPM or DPM).
Count and record other samples. Contamination control
Recount samples, 20+ hours after collection.
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Calculate and Evaluate
Compare incident scene samples to upwind/background sample.
Expect air samples from all locations to show significant alpha and beta activity from radon daughters.
If sample < background results, then airborne contaminant unlikely.
If sample > twice background results, then airborne contamination exists.
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Calculate and Evaluate
If background < sample < twice background …grey area.
Use field gamma spectrometry (SAM-935 or GR-135) to identify (if possible) the radionuclide detected on the air filters. Capture/record spectrum.
Expect to see gammas from radon daughters.
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Calculate DAC Level
Health Physics assistance recommended at this point.
Radon and daughter products complicate the calculation and interpretation of air sample results. Can mask the presence of a contaminant.
Continue to wear respiratory protection until sample analysis and data interpretation are complete.
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Calculate DAC
DAC: Derived Air Concentration 10 CFR 20 – Appendix B
Inhalation of 1 DAC for 1 year (2000 hrs) leads to a dose of 5 rem.
Varies by radionuclide and chemical form –D, W, Y clearance class.
Sum of fractions rule for multiple radionuclides.
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Calculate DAC Fraction
Quantify amount of radionuclide on air filter-spectrometer, lab analysis, assumptions, experience, … etc.
Calculate airborne concentration Cx(µCi/cc).
Consult reference 10 CFR 20, App B, Table 1 Cx / DACx = DAC fraction
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DAC(s) and Dose
Inhalation dose is tabulated/tracked by DAC hrs: 4 hours at 50% DAC = 2 DAC-hrs
1 DAC-hr = 2.5 mrem
Respirator protection factors reduce or eliminate inhalation dose.
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Demonstration
Set up an H-810 air sampler. Program the unit to collect a 120 cubic foot
sample of potential Am-241 in air. Operate the air sampler. Retrieve the sample when sampling is
completed. Package sample, submit for analysis. Take air sampler unit down. Count the sample, calculate the fraction of
the DAC (assume Am-241).
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Soil Sampling Considerations
Current Rad Playbook, FRMAC, etc., call for 10 x 10 cm sampler at 1”. Use the “scoop”.
Depending on time in response larger or deeper sample may be required.
Sampling in open areas best. Vegetation and rocks in sample not a good
idea. Decon of tools is really important. Care is needed in collection in bagging,
tagging, etc.
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Soil Sampling Considerations
Frozen ground a problem! Wet ground potentially a problem! Sandy ground potentially a problem! It may
not ‘scoop’! Bottom line: use your common sense Note special circumstances on sample form Note radiation readings on samples from
surface of bag and handle accordingly.
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Questions?