What is the right instrument?
3. For contamination monitoring?

For each of the three types of potential contaminant, α, β and X or γ photon, there is a variety of types of instrument available.
Potential alpha contamination
- Alpha emissions are characterised by their extremely short range (a few mm in air) and the very high rate of energy deposition.
- Monitors require very thin windows (approximately 1 mg cm-2) to allow the particle to pass into the detecting volume but then have very high rates of energy deposition within the detector which can be used to give good discrimination against signals produced by β and X or γ radiation.
- All monitors should have a very low background, typically a few counts per minute. If it is higher than normal, the probe is probably contaminated and should be cleaned.
Typical detectors include:
- zinc sulphide scintillation detectors
- dual phosphor detectors
- thin-window proportional counters
- pancake style GM detectors
Light leaks in scintillation detectors will generally show up as an increase in background. Scintillation detectors should have a light leak detection mechanism to avoid any failure to danger.
Potential beta contamination
- Beta contaminants found in practice range from 3H (Emax = 0.018 MeV) to 106Rh (Emax = 3.6 MeV).
- In the majority of circumstances, the lowest energies cannot be directly detected on a surface. 14C (Emax = 0.156 MeV) is the lowest energy b emitter that is normally considered to be detectable but even this is challenging.
Typical detectors include:
- scintillation detectors
- refillable or sealed proportional counters
- thin-end-window or thin-walled GM detectors
Light leaks in scintillation detectors will generally show up as an increase in background. Scintillation detectors should have a light leak detection mechanism to avoid any failure to danger.
NOTE
Some instruments discriminate between alpha and beta contamination -Dual Alpha and Beta contamination probes
- These instruments display alpha and beta count rates in separate channels.
- While the contribution of beta radiation to the alpha channel should be negligible, the alpha activity will normally contribute significantly to the beta channel count rate.
- Correct setting of the operating point is even more important for dual probes than for separate alpha and beta probes.
Potential X, γ contamination
- Many radionuclides emit γ radiation. This emission is normally preceded or accompanied by the emission of a β particle or other radiation.
- Contamination is normally monitored using the β emissions rather than the γ radiation because β monitors have lower background count rates, higher detection efficiencies and a response that is far less influenced by activity not directly under the detector. The only circumstance when the γ emissions are normally used for the monitoring is when there is contamination in bulk. This situation will not be considered here.
There are two popular types of detector for monitoring contamination by electron capture nuclides:
- thin-windowed sodium iodide scintillation detectors
- titanium windowed xenon filled proportional counters.
Both types of detector have a good X and γ detection efficiency but the lower energy threshold varies with window type and should be confirmed. The X-rays are only weakly attenuated by air, which means that monitoring can take place with the probe at a distance from the surface of interest.
The main problem tends to be the presence of other sources in the area, producing a high local background making the detection of contamination more difficult. One option is to use a detector, which has a lead sleeve surrounding the scintillator (sometimes described as collimated detectors). Their use will reduce the background where the source of radiation is well off the axis of the detector, e.g. a source safe in a distant corner of the bench being monitored. The disadvantage of collimated detectors is that they are heavier.
Good practice online modules
- Practical radiation monitoring
- Practical radiation monitoring units
- Radiation monitoring strategy
- Choice of radiation instrument
- Radiation monitoring techniques
- Estimating surface radioactivity
- Radiation instrument calibration
- Uncertainties in radiation measurement
- Troubleshooting in radiation monitoring
