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E.I.M. Meijne NRG Radiation & Environment The Netherlands
Operational aspects of decommissioning installations containing mineral wool E.I.M. Meijne NRG Radiation & Environment The Netherlands
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Contents Dutch legislation with respect to mineral wool
What is mineral wool? Dutch legislation with respect to mineral wool Decommissioning of a fossil fuelled power plant operational aspects estimated doses waste handling Conclusions
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What is mineral wool? Insulation material produced from slag
Slag wool is produced from tin slag and contains enhanced concentration NORM Produced in The Netherlands from Typical brown colour, tight glass-like matrix [Th-232sec] = 11.2 and [U-238sec] = 4.0 Has been used as insulation materials in a number of different types installations: in ovens, doors, steam generators, boilers e.a.
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Dutch legislation relevant to slag wool
Nuclide specific exemption/clearance levels Exemption level = clearance level Sum rule applies Weighted sum: > 1 and < reporting requirements (not yet published) > authorisation required Disposal options waste sum > COVRA sum > 1 and < dedicated landfill or incinerator sum < no restriction from a radiological/legal point of view
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Application of exemption levels to slag wool
Nuclide Measured concentration (Bq/g) Exemption value (Bq/g) Contribution to weighted sum U-238sec Th-232sec Total 4.0 11.2 1 4.0 11.2 15.2 Possessing, handling and disposal of slag wool requires authorisation Dismantling requires radiation protection measures Waste considered as radioactive waste
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Decommissioning of a fossil-fuelled power plant
Started in 1998 presence of radioactive material unknown In 1999 dismantling of boiler I and II started Scrap with adherent slag wool triggered a portal monitor at a scrap yard Inspectorate was notified Dismantling stopped immediately Investigation was carried out
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Building was already partly demolished
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Covering of boilers was partly removed exposing the slag wool
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Slag wool was spread over the entire plant
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Actions taken Work plan prepared describing the activities and radiation protection measures to be taken Authorisation obtained for remediation and further decommissioning - activities were carried out under the permit of NRG Survey was made of the entire plant to identify slag wool containing parts of the installation (Microcont H-13420, Xenon filled) Measures were were taken to prevent further spreading of the slag wool
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Slag wool insulated demi-water tanks
Measured dose rates On surface tank: 970 nSv/hr At 1 m: nSv/hr
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Slag wool insulated coal feed bunkers
Measured dose rates On surface bunker: 1000 nSv/hr At 1 m: nSv/hr
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Measures taken to prevent spreading of slag wool to the environment
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Measures taken to prevent spreading of slag wool to the environment
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PPE used: RPE: full-face mask (power assisted) Disposable coveralls
Gloves Safety boots
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Measures taken to prevent spreading of slag wool in the building
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Measures taken to prevent further spreading of slag wool in the building
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Collection of slag wool
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Dose coefficients for inhalation of nuclides from slag wool and those listed in BSS
Lung class DC Sv/Bq BSS lung class DC Sv/Bq Ratio DC slag wool / BSS U-238++ Ra-226+ Pb-210+ Po-210 Th-232 Ra-228+ Th-228+ S 2.6 E-5 4.0 E-5* 4.9 E-6 3.2 E-6 1.2 E-5 1.3 E-5 3.5 E-5 M F 2.2 E-6 1.2 E-6 1.8 E-6 18.0 4.1 1.5 7.2 U = U-238, Th-234, Pa-234m, U-234, Th-230 and U-235 (4.5%) * = (no radon emanation)
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Dose coefficients for inhalation of slag wool based on 5 µm AMAD and type Slow
Nuclide DC in Sv/Bq Average conc. in slag wool (Bq/g) DC in Sv/g U Ra-226 Pb Po-210 Th Po-212 6.6 E-5 8.1 E-6 6.0 E-5 4 3 11 2.6 E-4 2.4 E-5 6.6 E-4 Total dose 9.5 E-4
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Estimated exposure during decommissioning of the power plant under various conditions
Respiratory Protective Equipment (RPE) Protection factor Internal exposure mSv External exposure mSv Total exposure mSv no 2.27 0.30 2.58 Full-face masks* 2000 (NPF) 40 (APF) 0.001 0.057 0.30 0.30 0.36 Exposure time: 1000 hours, dust concentration: 2 mg/m3
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Slag wool remaining after decommissioning
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Slag wool remaining after decommissioning
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Compression of the slag wool
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Containers containing compressed slag wool
Measured dose rates On surface containers: µSv/hr At 1 m: µSv/hr
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Temporary storage of slag wool
Dose rate at fence : 150 nSv/hr
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Appearance of slag wool after compression
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Conclusions Slag wool containing installations require an authorisation DCs for radionuclides from slag wool are higher than those listed in the BSS Proper radiological protection measures avoid potentially significant exposure during dismantling Main problems are the unawareness at the start of the decommissioning and disposal of the slag wool Volume reduction by compression results in pulverisation of the wool and is thus not preferable if reuse options are possible The negative public opinion regarding radioactive material complicates the development of reuse options even if the resulting doses are negligible.
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