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KMID : 1039220170270010038
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Journal of Korean Society of Occupational and Environmental Hygiene
2017 Volume.27 No. 1 p.38 ~ p.45
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Evaluation of Effective Dose and Exposure Levels of Radon in Office and Plant Buildings
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Chung Eun-Kyo
Kim Ki-Woong
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Abstract
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Objectives: Radon may be second only to smoking as a cause of lung cancer. Radon is a colorless, tasteless radioactive gas that is formed via the radioactive decay of radium. Therefore, radon levels can build up based on the amount of radium contained in construction materials such as phospho-gypsum board or when ventilation rates are low. This study provides our findings from evaluation of radon gas at facilities and offices in an industrial complex.
Methods: We evaluated the office rooms and processes of 12 manufacturing factories from May 14, 2014 to September 23, 2014. Short-term data were measured by using real-time monitoring detectors(Model 1030, Sun Nuclear Co., USA) indoors in the office buildings. The radon measurements were recorded at 30-minute intervals over approximately 48 hours. The limit of detection of this instrument is 3.7 ㏃/㎥. Also, long-term data were measured by using α-track radon detectors(α-track, Rn-tech Co., Korea) in the office and factory buildings. Our detectors were exposed for over 90 days, resulting in a minimum detectable concentration of 7.4 ㏃/㎥. Detectors were placed 150-220 cm above the floor.
Results: Radon concentrations averaged 20.6 ± 17.0 ㏃/㎥(3.7-115.8 ㏃/㎥) in the overall area. The monthly mean concentration of radon by building materials were in the order of gypsum>concrete>cement. Radon concentrations were measured using α-track in parallel with direct-reading radon detectors and the two metric methods for radon monitoring were compared. A t-test for the two sampling methods showed that there is no difference between the average radon concentrations(p<0.05). Most of the office buildings did not have central air-conditioning, but several rooms had window- or ceiling-mounted units. Employees could also open windows. The first, second and third floors were used mainly for office work.
Conclusions: Radon levels measured during this assessment in the office rooms of buildings and processes in factories were well below the ICRP reference level of 1,000 ㏃/㎥ for workplaces and also below the lower USEPA residential guideline of 148 ㏃/ ㎥. The range of indoor annual effective dose due to radon exposure for workers working in the office and factory buildings was 0.01 to 1.45 m㏜/yr. Construction materials such as phospho-gypsum board, concrete and cement were the main emission sources for workers` exposure.
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KEYWORD
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Becquerel(㏃), construction materials, radon exposure, effective dose
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