• 제목/요약/키워드: 라돈 및 토론

검색결과 5건 처리시간 0.021초

한국원자력연구원 새빛연료과학동 굴뚝방출 방사능 평가 (Evaluation of Radioactive Stack Air Effluents from the Advanced Fuel Science Building at KAERI)

  • 장시영;김봉환
    • Journal of Radiation Protection and Research
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    • 제33권3호
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    • pp.121-126
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    • 2008
  • 한국원자력연구원 새빛연료과학동의 굴뚝에서 대기로 방출되는 배기의 방사능을 측정, 분석 및 평가하였다. 동 시설에서는 연구용원자로 하나로의 핵연료를 생산하는 외에 첨단 핵연료를 연구하고 있으며 환경을 보호하기 위하여 시설외부로 방출되는 굴뚝배기 방사능 감시기를 연속 가동하고 있다. 2008년 1월 $\sim$ 3월동안 굴뚝배기 방사능 감시기의 밀리포어 집진+CY8필터에 포집된 방사능과 핵종을 정기적으로 측정하고 핵종을 분석한 결과, 천연방사성 핵종인 라돈($^{222}Rn$)과 토론($^{220}Rn$)의 단 반감기의 딸핵종들 및 40K이 미량으로 검출되었으나 72시간 이내에 계측기의 최소검출방사능(MDA) 이하로 붕괴하였으며 우라늄 핵종은 검출되지않았다. 이로서 한국원자력연구원 새빛연료과학동으로부터 우라늄 핵종은 대기중으로 방출되지 않는 것으로 평가되었다.

일부 생활용품에서 발생한 공기 중 라돈과 토론의 발생 특성 및 연간 유효선량 추정 (Effective Doses Estimated According to Characteristics of Airborne Radon and Thoron Levels Generated from Some Household Products)

  • 박동욱;이성진;김소연;곽현석;이승희;박지훈
    • 한국환경보건학회지
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    • 제45권2호
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    • pp.99-112
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    • 2019
  • Objective: This study aims to analyze the characteristics of airborne radon and thoron level ($Bq/m^3$) generated from household products containing monazites, and estimate the effective doses (mSv/yr). Method: Radon & Thoron detector EQF3220 was used to monitor real-time airborne radon and thoron level ($Bq/m^3$), and their daughters ($Bq/m^3$) were recorded every two hours. Effective doses (mSv/yr) for radon and thoron were estimated according to models developed by International Commission on Radiological Protection (ICRP) and United Nations Scientific Committee on the Effects of Atomic Radiation (UNSCEAR). Results: The average levels of radon and thoron were $87.8Bq/m^3$ (range; $20.8-156.3Bq/m^3$) and $1,347.5Bq/m^3$ (range; $4-5,839.7Bq/m^3$), respectively. The average equilibrium factors (F) were 0.23 and 0.007, respectively. The levels of radon progeny were far higher than that thoron. Latex mattress showed the highest F (0.38). The average effective doses were estimated to be ICRP (1.9 mSv/yr) and UNSCER (1.3 mSv/yr) for radon and UNSCEAR (1.6 mSv/yr) for thoron. Conclusions: Our results have far exceeded the allowable effective dose for general population (1 mSv/yr). The government's actions such as the ban of use of consumer products containing monazite and the establishment of surveillance system to evaluate health effects for the people affected should be taken as early as possible.

모나자이트 취급공정에서의 라돈 및 토론 노출 특성 (Characteristics of Internal and External Exposure of Radon and Thoron in Process Handling Monazite)

  • 정은교
    • 한국산업보건학회지
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    • 제29권2호
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    • pp.167-175
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    • 2019
  • Objectives: The purpose of this study was to evaluate airborne radon and thoron levels and estimate the effective doses of workers who made household goods and mattresses using monazite. Methods: Airborne radon and thoron concentrations were measured using continuous monitors (Rad7, Durridge Company Inc., USA). Radon and thoron concentrations in the air were converted to radon doses using the dose conversion factor recommended by the Nuclear Safety and Security Commission in Korea. External exposure to gamma rays was measured at the chest height of a worker from the source using real-time radiation instruments, a survey meter (RadiagemTM 2000, Canberra Industries, Inc., USA), and an ion chamber (OD-01 Hx, STEP Co., Germany). Results: When using monazite, the average concentration range of radon was $13.1-97.8Bq/m^3$ and thoron was $210.1-841.4Bq/m^3$. When monazite was not used, the average concentration range of radon was $2.6-10.8Bq/m^3$ and the maximum was $1.7-66.2Bq/m^3$. Since monazite has a higher content of thorium than uranium, the effects of thoron should be considered. The effective doses of radon and thoron as calculated by the dose conversion factor based on ICRP 115 were 0.26 mSv/yr and 0.76 mSv/yr, respectively, at their maximum values. The external radiation dose rate was $6.7{\mu}Sv/hr$ at chest height and the effective dose was 4.3 mSv/yr at the maximum. Conclusions: Regardless of the use of monazite, the total annual effective doses due to internal and external exposure were 0.03-4.42 mSv/yr. Exposures to levels higher than this value are indicated if dose conversion factors based on the recently published ICRP 137 are applied.