Occupational Intakes of Radionuclides Part 1 - ICRP
Occupational Intakes of Radionuclides Part 1 - ICRP
Occupational Intakes of Radionuclides Part 1 - ICRP
Create successful ePaper yourself
Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.
3693<br />
3694<br />
3695<br />
3696<br />
3697<br />
3698<br />
3699<br />
3700<br />
3701<br />
3702<br />
3703<br />
3704<br />
3705<br />
3706<br />
3707<br />
3708<br />
3709<br />
3710<br />
3711<br />
3712<br />
3713<br />
3714<br />
3715<br />
3716<br />
3717<br />
3718<br />
3719<br />
3720<br />
3721<br />
3722<br />
3723<br />
3724<br />
3725<br />
3726<br />
3727<br />
3728<br />
3729<br />
3730<br />
3731<br />
3732<br />
3733<br />
3734<br />
DRAFT REPORT FOR CONSULTATION<br />
difficulties in assessing intakes from PAS measurements were considered by Whicker<br />
(2004). Breathing zone measurements can vary significantly as they can be affected<br />
by measurement conditions such as orientation <strong>of</strong> the sampler with respect to source,<br />
on which lapel (right or left) the sampler is worn, design <strong>of</strong> the air sampling head,<br />
particle size, local air velocities and directions, and sharp gradients in and around the<br />
breathing zone <strong>of</strong> workers.<br />
(263) Britcher and Strong (1994) reviewed the use <strong>of</strong> PAS as part <strong>of</strong> the internal<br />
dosimetry monitoring programmes for the Calder Hall reactors and the Sellafield<br />
nuclear fuel reprocessing facility in the U.K. It was concluded that samplers can be<br />
used to obtain satisfactory estimates <strong>of</strong> intake for groups <strong>of</strong> workers. However, for<br />
individuals, the correlation between assessments using PAS and biological samples<br />
was poor and the authors cast doubt on the adequacy <strong>of</strong> PAS for estimating annual<br />
intakes <strong>of</strong> individual employees at the levels <strong>of</strong> exposure encountered in operational<br />
environments. The authors also questioned whether, for environmental monitoring,<br />
PAS <strong>of</strong>fered any advantages over static air sampling programmes. The same lack <strong>of</strong><br />
correlation between PAS and bioassay sample-based intake estimates was also seen<br />
for known acute exposures (Britcher et al, 1998).<br />
(264) A uranium exposure study was conducted by Eckerman and Kerr (1999) to<br />
determine the correlation between uranium intakes predicted by PASs and intakes<br />
predicted by bioassay at the Y12 uranium enrichment plant in Oak Ridge, USA. This<br />
study concluded that there was poor correlation between the two measurements.<br />
(265) Static air samplers are commonly used to monitor workplace conditions, but<br />
can underestimate concentrations in air in the breathing zone <strong>of</strong> a worker. Marshall<br />
and Stevens (1980) reported that PAS:SAS air concentration ratios can vary from less<br />
than 1 up to 50, depending on the nature <strong>of</strong> the work. Britcher and Strong ( 1994)<br />
concluded from their review <strong>of</strong> monitoring data for Magnox plant workers in the U.K.<br />
that intakes assessed from PAS data were about an order <strong>of</strong> magnitude greater than<br />
those implied by SAS data. SAS devices, however, can provide useful information on<br />
radionuclide composition, and on particle size, if used with a size analyzer such as a<br />
cascade impactor.<br />
(266) Overall, the use <strong>of</strong> PASs and SASs can be an important part <strong>of</strong> a<br />
comprehensive workplace monitoring programme and is able to provide an early<br />
indication <strong>of</strong> risk <strong>of</strong> exposure. Experience <strong>of</strong> the use <strong>of</strong> PASs and SASs indicates that<br />
body activity measurements and/or excreta analysis are to be preferred for the<br />
assessment <strong>of</strong> individual intakes <strong>of</strong> airborne radionuclides and doses.<br />
(267) However, for some transuranic radionuclides, body activity measurements and<br />
urine analysis can only quantify exposures sufficiently reliably above a few mSv<br />
unless sensitive mass spectrometric techniques for the analysis <strong>of</strong> bioassay samples<br />
are available. For the detection <strong>of</strong> lower exposures, a combination <strong>of</strong> monitoring<br />
methods is then likely to be needed, which could include air sampling and faecal<br />
analysis.<br />
106