• Title/Summary/Keyword: 드럼핵종분석장치

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고순도게르마늄(HPGe) 검출기를 이용한 방사성폐기물 드럼의 핵종농도 평가

  • 박경록;강덕원
    • Proceedings of the Korean Nuclear Society Conference
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    • 1996.11b
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    • pp.583-589
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    • 1996
  • 원자력발전소에서 발생되는 방사성폐기물들은 폐기물형태 및 방사능 농도가 다양하며 영구처분장으로 이송전까지는 발전소내의 임시 저장고에 안전하게 보관, 관리하고 있다. 생성된 폐기물드럼내에는 감마방출핵종을 비롯하여 알파 및 베타방출 핵종들이 균질 또는 비균질하게 존재하고 있으며 방사능의 세기나 폐기물의 특성에 따라 안정화시키거나 압축처리하여 드럼에 담겨져 있기 때문에 일반적인 파괴분석에 의한 화학분석법으로는 작업자의 피폭, 시료의 대표성 선정 및 장시간의 화학처리 시간소요 등으로 핵종분석이 곤란하다. 따라서 본 논문은 일반적으로 감마핵종분석시 흔히 사용하고 있는 고순도게르마늄(HPGe) 검출기를 이용하여 드럼의 감마핵종농도를 분석하는 방법과 장치의 개발에 대해 언급하였으며 알파나 베타핵종과 같이 직접 분석이 곤란한 핵종들은 각 폐기물드럼내에 존재하는 Co-60이나 Cs-137과의 상관관계를 미리 예측한 척도인자 (scaling factor)를 이용하여 간접적으로 구하는 방법을 사용하고 있으나 본 논문에서는 드럼으로부터 감마핵종만을 분석하는 방법에 대해서만 언급하였다. 또한 핵종분석시스템의 최적 운전조건을 도출하기 위해 드럼회전테이블의 속도결정 및 모의드럼을 이용한 방사능측정 등을 통해 핵종 농도 분석시의 오차를 30% 이내로 유지할 수 있었다.

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표면선량율을 이용한 방사성폐기물 드럼내 핵종평가

  • 강덕원;신상운;박경록
    • Proceedings of the Korean Nuclear Society Conference
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    • 1995.05a
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    • pp.872-878
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    • 1995
  • 방사성폐기물 드럼내에 포함되어 있는 방사성 핵종의 양이 핵종분석장치로 측정할 수 있는 검출 하한치 이하이거나, 혹은 너무 높아 불감시간이 크게 증가될 경우에는 순수 Ge 검출기를 장착한 핵종분석장치로는 분석이 불가능하게 되므로 본 연구에서는 표면선량율과 Scaling Factor를 이용하여 드럼속에 포함되어 있는 핵종들의 양을 평가하는 방법을 제시하였으며, 불균일성이 높을 경우의 가능한 평가방법을 알아보기 위하여 점선원을 이용한 실험을 실시하였다. 그 결과 비균질 드럼에 대해서는 점선원을 이용한 자료를 이용하는 것이 합리적이고 기하학적 산술평균을 취함으로써 보다 정확도가 증가됨을 알 수 있었다. 그러나 그 오차범위는 -25%∼5.5%로서 실제보다 상당히 낮게 평가되는 경향이 있으므로 적절한 비균질성 보정인자를 적용할 필요가 있는 것으로 생각된다.

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방사성폐기물 핵종 분석장치 개발

  • 강덕원
    • Nuclear industry
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    • v.16 no.12 s.166
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    • pp.70-77
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    • 1996
  • 원자력발전소에서 발생되는 방사성 폐기물 드럼 안에 있는 핵종과 그 양을 비파괴적인 방법으로 분석할 수 있는 방사성 폐기물 핵종 분석 장치가 개발되었다. 한전 전력연구원이 한국원자력연구소와 공동으로 개발한 이 장치는 기존의 계측 방법과 달리 슬라이드형 콜리메이터를 이용해 방사선량률 변화에 따라 드럼 안의 고방사능량까지 효율적으로 측정할 수 있는 시스템을 갖추고 있다. 현재 이 시스템은 실험실 성능 시험을 마치고 고리 제4폐기물 저장고에 설치되어 시험 운전중이며, 성능 검증 시험을 마친 후 전 원전에 설치될 예정이다.

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Determination of Attenuation Collection Methods According to the Type of Radioactive Waste Drums (방사성폐기물드럼 종류별 감쇠보정방법의 결정)

  • Kwak, Sang-Soo;Choi, Byung-I1;Yoon, Suk-Jung;Lee, Ik-Whan;Kang, Duck-Won;Sung, Ki-Bang
    • Journal of Radiation Protection and Research
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    • v.22 no.4
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    • pp.309-317
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    • 1997
  • The measured radioactivity of gamma-emitting radionuclides in each radioactive waste drum using the non-destructive waste assay method is underestimated than real radioactivity in radioactive waste drum because the gamma-rays are attenuated within the medium. Therefore, the measured radioactivity should be corrected for the attenuation of gamma-rays. For the correction of the attenuation of gamma-rays, the attenuation correction method should be applied differently by considering the distribution and density of medium in radioactive wastes drum generated from nuclear power plants. In this study, the model drums were fabricated for simulating five types of radioactive waste drums generated from nuclear power plant and the optimum methods of the attenuation correction were experimentally determined to analyze the activity of radionuclides in the waste drum accurately using the segmented gamma scanning system. With the determination of the attenuation correction methods from the experimental results the transmission method and the average density method for the miscellaneous waste drum, the transmission method and the differential peak absorption method for the shielded miscellaneous waste drum were used to measure the density of medium in waste drums. Also, the average density method and the differential peak absorption method for the spent resin drum, the paraffin solidified drum, and the spent filter drum were used.

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An Evaluation on the Radiation Shielding of the Radwaste Drum Assay Facility (방사성폐기물드럼 핵종재고량 평가시설 구축에 따른 방사선차폐 영향평가)

  • Ji, Young-Yong;Kwak, Kyung-Kil;Hong, Dae-Seok;Shon, Jong-Sik
    • Journal of Nuclear Fuel Cycle and Waste Technology(JNFCWT)
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    • v.10 no.2
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    • pp.117-123
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    • 2012
  • In order to dispose of the LILW(low and intermediate level radioactive waste) stored at KAERI, the radwaste drum assay system will be introduced to evaluate the radioisotopes inventory of stored drums. At present, the construction project of the dedicated assay facility to operate it and carry out routine maintenance of that equipment has been conducting at the radwaste treatment facility. Since that facility will be constructed in front of a 1st radwaste storage facility as well as the radwaste drums to be assayed and the transmission source in the radwaste drum assay system are in that facility, they could act as the radioactive sources and then, would affect the dose rate at the inside and the outside of the facility. Therefore, the radiation shielding should be evaluated through the concrete wall near to the radioactive sources whether the wall thickness is sufficient against the regulations. In this study, the radiation safety for the concrete wall around the radiation controlled area in the radwaste drum assay facility was evaluated by the MCNP code. From the evaluation results, the thickness of those concrete walls which are under consideration of about 30 cm was enough to shield the radiation from the radioactive sources.

Development of Radionuclide Inventory Declaration Methods Using Scaling Factors for the Korean NPPs - Scope and Activity Determination Method - (국내 원전 대상의 척도인자를 활용한 핵종재고량 규명 방법의 개발 - 범위 및 방사능 결정 방법-)

  • Hwang, Ki-ha;Lee, Sang-chul;Kang, Sang-hee;Lee, Kun-Jai;Jeong, Chan-woo;Ahn, Sang-myeon;Kim, Tae-wook;Kim, Kyoung-doek;Herr, Young-hoi
    • Journal of Nuclear Fuel Cycle and Waste Technology(JNFCWT)
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    • v.2 no.1
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    • pp.77-85
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    • 2004
  • Regulations and guidelines for radioactive waste disposal require detailed information about the characteristics of radioactive waste drums prior to transport to the disposal sites. However, estimation of radionuclide concentrations in the drummed radioactive waste is difficult and unreliable. In order to overcome this difficulty, scaling factor (SF) method has been used to assess the activities of radionuclides, which could not be directly analyzed. A radioactive waste assay system has been operated at Korean nuclear power plant (KORI site) since 1996 and consolidated SF concept has played a dominant role in the determination of radionuclide concentrations. However, SFs are somewhat dispersive and limited in KORI site. Therefore establishment of the assay system using more improved SFs is planned and progressed. In this paper, the scope of research is briefly introduced. For the selection of more reliable activity determination method, the accuracy of predicted SF values for each activity determination method is compared. From the comparison of each activity determination method, it is recommended that SF determination method should be changed from the arithmetic mean to the geometrical mean for more reliable estimation of radionuclide activity. Arithmetic mean method and geometric mean method are compared based on the data set in KORI system. And, this change of SF determination method will prevent an inordinate over-estimation of radionuclide inventory in radwaste drum.

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Current Status of the Spent Filter Waste and Consideration of Its Treatment Method in KAERI (KAERI 저장 폐필터의 현황과 처리방법에 관한 고찰)

  • Ji, Young-Yong;Hong, Dae-Seok;Kang, Il-Sik;Shon, Jong-Sik
    • Journal of Nuclear Fuel Cycle and Waste Technology(JNFCWT)
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    • v.5 no.3
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    • pp.257-265
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    • 2007
  • Spent filter wastes of about 1,000 units (200 L) have been stored in the waste storage facility of the Korea Atomic Energy Research Institute since its operation. At the moment, to secure space in a waste storage facility as well as to efficiently manage spent filter wastes, it is necessary to conduct a compaction treatment of these spent filters, and finally, to repack the compacted spent filters into a 200 liter drum. To do that, the spent filter wastes were first classified according to their generation facilities, their generation date and their surface dose rate by investigating the inventory of the spent filters. In order to repack a compacted spent filter in a 200 liter drum, it is first necessary to conduct a radionuclide assessment of a spent filter before compacting it. Therefore, after taking a representative sample from a spent filter without a dismantlement, the nuclide analysis for it will be conducted. And then, after putting a spent filter into a regular drum by conducting the columnar shaping of the hexahedral form of a spent filter, the compaction treatment of the shaped spent filter will be conducted by vertically compacting it.

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