Answer to Question #6694 Submitted to "Ask the Experts"
Category: Instrumentation and Measurements — Instrument Calibration (IC)
The following question was answered by an expert in the appropriate field:
Q
Calibration standards for solid and liquid geometries are available in
plenty, whereas availability of gaseous standards especially for FPNG
(fission product noble gases) is almost rare, and getting the same in
the required geometry is also difficult. I have done some experiments
with radon, which is a gaseous source and whose daughters do have plenty
of gamma energies covering a range of 200 keV to 2,500 keV. I have
injected the radon gas into a one-liter PVC (polyvinyl chloride) bottle
and I have continuously obtained a gamma spectrum of the same for about
five times over a period of one week. After that, I have sampled and
determined the radon activity present in the bottle using a Lucas
(alpha scintillation counting with ZnS) cell. Once radon activity is
calculated, the daughter activities present in the bottle at different
periods of time can be calculated. Efficiency for each energy can be
determined and the same can be plotted. Using an energy versus
efficiency plot, the efficiency for the energy required can be
calculated. Kindly let me know whether my approach is correct or not.
A
While you can purchase some fission product noble gases in known
quantities, it is true that you may have problems getting all you need
and in obtaining them in the geometries desired.
The approach you have outlined would be appropriate if there was a way
to ensure that the radon progeny would remain airborne in the bottle
over the period of your measurements. Unfortunately, this is not likely
the case, and daughter products will deposit on the inner surface of
the bottle, thus changing the counting geometry compared to what is
observed if all products remain airborne. The degree of impact that the
change in geometry has on the observed counting efficiency depends on a
number of factors, including the size and shape of the bottle and the
distance and orientation of the bottle with respect to the detector.
As you know, the major radionuclides that contribute significant gamma rays are the metal ions/atoms of 214Pb (half-life of 26.8 min) and 214Bi
(half-life of 19.9 min), and these are subject to deposition on the
walls of the container. You may be able to get an idea of how much the
deposited progeny are contributing to counts in the gamma spectrum at a
given elapsed time past filling with radon by counting the bottle
containing the radon and progeny at an elapsed time of interest, then
flushing the radon and airborne progeny from the bottle with clean air
and recounting it to observe the gamma pulse height distribution from
the deposited progeny.
If one corrects for individual decay of the progeny, one would expect
the fractional deposition of the progeny to increase with increasing
elapsed time up to a half day or so and then to level off as an
equilibrium situation takes place in which deposited activity is
decaying as rapidly as new activity is being deposited.
If you don't correct for decay, the observed deposition will appear to
increase, go through a maximum, and then decrease over several hours.
(In order to observe such behavior you would have to take numerous
measurements over a number of hours, each time having filled the bottle
with a fixed amount of radon and allowed a specified amount of time to
elapse before flushing out the radon and counting the deposited
progeny.)
If you find that the deposited progeny are contributing a negligible
fraction of the observed total counts, then you can neglect their
effect on the counting efficiency. If the counts contributed by
deposited progeny are significant, you can attempt to correct for their
effect by subtracting counts observed for the deposited progeny in each
respective energy region of interest from the total counts (before
flushing out the radon) in the same respective regions of interest.
Naturally you must decay correct each radionuclide to the same point in
time before doing the subtraction. There may be some error in this
method because the process of flushing out the radon and airborne
progeny from the bottle may produce some additional deposition of
progeny because of the turbulence effect that might result from the
flushing. I do not think the turbulent deposition would be a severe
effect if the flushing is done quickly.
Good luck in your attempts to evaluate the efficiencies you require.
George Chabot, PhD, CHP
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