Title: ICNTS conference, ID 191
1ICNTS conference, ID 191
- Alpha-track radon measurements at very low and
high exposures - by
- Tryggve Rönnqvist, PhD
- Gammadata Mätteknik AB, Uppsala, Sweden
2Gammadata
Gammadata was founded 1986 by scientists from
Uppsala University in order to measure the
radioactive fall-out from the reactor at
Chernobyl.
In 1988 Gammadata expanded its measurement
services to include radon measurements in
dwellings and workplaces. A development of
electronic instrumentation for radon detection in
air and soil was also initiated.
Today Gammadata consists of three major parts
with about 180 employees in total. Gammadata
Mätteknik AB handles the measurement services and
consists of 15 employees.
To date approximately 450000 cesium tests and
more than 1000000 passive radon detectors have
been measured in this accredited laboratory.
3Measurement of radon in airClosed alpha-track
film with filter
- Function
- Radon gas enters the detector through the small
gap between the bottom and top of the detector
holder. No radon decay products can enter the
detector from the outside (filter). - In the detector an alpha-track film (CR-39) is
located which is sensitive to alpha decay. The
measured area of the film is about 1,4 cm2. - The detector holder is manufactured in
electrically conducting plastic in order to avoid
problems with static electricity.
4Measurement of radon in airClosed alpha-track
film with filter
- Long-term measurement
- Measurement period at least 2 months (3 months
recommended). - Ageing effects have little influence. No major
problems to store the detectors (recommended
storage time, max. 1,5 years). - Short-term measurements
- Larger detector holder (RAPIDOS) provides better
counting statistics and a better signal to noise
relation. - Measurement period at least 7 days (usually 10
days). - The detectors should not be stored for a longer
time (max. 8 months).
5Measurement uncertainties Long-term radon
measurements
6Measurement uncertaintiesShort-term measurements
7Measurement of radon in airHigh exposures
- Counting method at high exposures
- Gammadata has developed and calibrated an
accredited counting method for radon exposures up
to 50000 kBqh/m3. - The method is based on counting the total
radiated area of the alpha-track film with
compensations made for the size of individual
tracks on the film. - The method is used when individual tracks overlap
to much, typically in the exposure range
7000-50000 kBqh/m3. - Measurement uncertainties at high exposures
- The uncertainty of the method due to e.g.
different track sizes and exposures is usually
about 10 . - The counting method requires clean CR-39
plastic with a low background since no background
is removed with blob analysis.
8Measurement uncertaintiesMain contributions
- Long-term measurements (about 90 days)
- Exposure (kBqh/m3) Main uncertainty
contributions - 0-250 (0-120 Bq/m3) Background
- 250-450 (120-200 Bq/m3) Calibration background
- 450-6000 (200-2800 Bq/m3) Calibration
- gt 6000 (gt 2800 Bq/m3) High exposure method
- Short-term measurements (about 10 days)
- Exposure (kBqh/m3) Main uncertainty
contributions - 0-40 (0-170 Bq/m3) Background transport
- 40-60 (170-250 Bq/m3) Background number of
tracks - 60-90 (250-380 Bq/m3) Calibration, background
tracks - 90-3000 (380-12500 Bq/m3) Calibration
- gt 3000 (gt 12500 Bq/m3) High exposure method
- (A calibration uncertainy of 5 is assumed.
Transport exposures can give contributions up to
5 kBqh/m3.)
9Measurement of radon in airQuality control of
CR-39 plastic
- Quality control of CR-39 plastic
- Gammadata has the following requirements on the
suppliers for each sheet of CR-39 plastic - Quality samples are etched and the sum of the
background level and background deviation should
be less than about 70 tracks/cm2. - The median value for the number of counts with
the high exposure counting method should be less
than about 200 counts/cm2. - In this quality control procedure some sheets are
rejected but the main part of the sheets (more
than 70) have a background level and a
background deviation less than 10 tracks/cm2
(recent productions from Intercast Europe). - Before producing the detectors, a new quality
control procedure is made where 4-5 of the films
are etched and measured. - Sheets with a very low background and with a
background deviation less than 10 tracks/cm2 are
approved for possible short-term measurements.
10Measurement of radon in airBackground calculation
- Considerations for background calculations
- The background level is mainly sheet dependent.
Therefore, the background level should be
calculated for each sheet of CR-39 plastic. - Enough films from each sheet should be used for
the background calculation in order to get good
statistics. The background films should be taken
from different parts of the sheet. - Due to aging effects and alpha-decay from the
detector holders, the background levels increase
with time. The background level should be
measured just before the exposed detectors will
be returned. - Gammadata use about 6 of the films for the
background calculation. Together with the quality
control more than 10 of the films are used for
quality control and background calculation. - Since the background increase with time,
detectors which should be used for short-term
measurements should have a short storage time.
11Summary
- Alpha-track radon measurements at low exposures
- In order to make radon measurements at low
exposures (out-door and short-term measurements)
with high quality, it is important to - Use CR-39 plastic with a low background since
the background level is the main uncertainty. - Use new detectors since the background
increase with time. - Determine the background level just before the
exposed detectors are returned. - Use enough films to get good statistics in the
quality control and background calculation. - Alpha-track radon measurements at high exposures
- In order to make radon measurements at high
exposures (gt 7000 kBqh/m3) with high quality, it
is important to - Use very clean and transparent CR-39 plastic.
- Make careful calibrations and tests of the
counting method.