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Occupational Intakes of Radionuclides Part 1 - ICRP

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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 />

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