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Biomedical subjects

P T Wasiolek

Publications and source records attributed to P T Wasiolek.

4 recordsLinked to original sources

Room airflow studies using sonic anemometry.

To ensure prompt response by real-time air monitors to an accidental release of toxic aerosols in a workplace, safety professionals should understand airflow patterns. This understanding can be achieved with validated computational fluid dynamics (CFD) computer simulations, or with experimental techniques, such as measurements with smoke, neutrally buoyant markers, trace gases, or trace aerosol particles. As a supplementary technique to quantify airflows, the use of a state-of-the art, three-dimensional sonic anemometer was explored. This instrument allows for the precise measurements of the air-velocity vector components in the range of a few centimeters per second, which is common in many indoor work environments. Measurements of air velocities and directions at selected locations were made for the purpose of providing data for characterizing fundamental aspects of indoor air movement in two ventilated rooms and for comparison to CFD model predictions. One room was a mockup of a plutonium workroom, and the other was an actual functioning plutonium workroom. In the mockup room, air-velocity vector components were measured at 19 locations at three heights (60, 120 and 180 cm) with average velocities varying from 1.4 cm s-1 to 9.7 cm s-1. There were complex flow patterns observed with turbulence intensities from 39% up to 108%. In the plutonium workroom, measurements were made at the breathing-zone height, recording average velocities ranging from 9.9 cm s-1 to 35.5 cm s-1 with turbulence intensities from 33% to 108%.

Aerosols↗

Experimental evaluation of wire mesh screen counting parameters for measurements of the unattached fraction of radon progeny.

Direct measurements (specifically the front-to-back ratio) of alpha radioactivity from radon progeny deposited on the front and back of a 400-wire mesh screen were performed under realistic aerosol conditions outdoors with two scintillation alpha detectors facing both sides of the screen simultaneously. Two flow regimes were tested: one which kept the flow Reynolds number (Ref) for the wire below one (200 L min-1) and a second with the flow Reynolds number for wire > 1 (400 L min-1). To estimate the radioactivity loss in the screen, parallel measurements of open and backup filters were also performed. The average front-to-back ratio expressed as a ratio of the potential alpha energy concentration as measured on the screen side facing the airflow to the other side of the screen for 200 L min-1 and 400 L min-1 was 3.42 +/- 0.32 (standard error) and 2.30 +/- 0.14 (standard error), respectively. The loss of radioactivity in the screen expressed as a ratio between the potential alpha energy concentration measured on an open filter minus backup filter to the sum of the potential alpha energy concentration measured on the front and back of the screen was 1.29 +/- 0.13 and 1.27 +/- 0.22 for 200 and 400 L min-1, respectively.

Evaluation Studies as Topic↗

Assessment of exposure to radon decay products in realistic living conditions.

The development of an automated system for activity-weighted size distribution measurements now permits more complete exposure and dose assessment for indoor radon decay products. Exposures characterized by the semi-continuous measurement of activity-weighted size distributions of radon decay products were obtained over four test periods in three normally occupied houses, two of which were occupied by cigarette smokers. These measured activity size distributions were used to calculate exposure-dose conversion coefficients and the annual effective doses. These doses were found to be approximately two-fold higher than the values derived conventionally from the measured radon concentration, on the assumption that indoor exposure to 20 Bq m-3 radon gas concentration corresponds to an annual effective dose 1 mSv y-1. The degree to which aerosol-measurement-based dose estimates were higher than radon-gas-based estimates was found to be influenced if the study house occupant was a cigarette smoker. Reassessment of the measured PAEC-weighted radon progeny particle size distribution in terms of the classical "unattached" and "attached" modes yielded lower estimates of the exposure-effective dose conversion coefficient that were similar to the reference values derived from a recent study by the National Research Council. Thus, by not resolving the measured radon progeny PAEC that is associated with particles intermediate in size between the two classical radon progeny modes, the estimated annual effective doses were also found to be similar to the values derived conventionally from the measured radon gas concentration. It is concluded that the observed presence of 4 to 13% of the radon progeny PAEC in the size-range 1.5 to 15 nm diameter is a dosimetrically significant factor that appears to be commonplace in various home environments.

Air Pollution, Indoor↗