Solid Radioactive Waste Strategy Report.pdf - UK EPR
Solid Radioactive Waste Strategy Report.pdf - UK EPR
Solid Radioactive Waste Strategy Report.pdf - UK EPR
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<strong>EPR</strong> <strong>UK</strong><br />
N° NESH-G/2008/en/0123<br />
REV. A PAGE 175 / 257<br />
Typically, the WTB will be directly connected to the nuclear auxiliary building of the <strong>UK</strong> <strong>EPR</strong>.<br />
All untreated solid wastes will be placed into temporary buffer stores prior to treatment. The<br />
waste will be separated into the different fractions dependent on the eventual treatment method.<br />
<strong>Waste</strong> will be stored in these areas until a sufficient quantity has accumulated for a treatment<br />
campaign to commence or for shipment for off-site treatment. Once a sufficient volume has<br />
been accumulated the waste is routed to the treatment system and the appropriate treatment is<br />
initiated.<br />
Records will be maintained describing the contents and composition of the waste at each<br />
treatment stage. This information will be stored in a central database and used to complete the<br />
appropriate storage, transfer and disposal documentation.<br />
During all handling operations the radiological properties of the wastes will be carefully<br />
considered and monitored and shielding and other measures provided to ensure that doses to<br />
operators are reduced. Examples of the types of safety features that will be incorporated into<br />
the design of the WTB are provided in this report.<br />
The layout of the WTB will be designed to facilitate contamination control. Areas with a high<br />
probability of the presence of loose contamination, for example inside the waste sorting box, will<br />
be individually connected to the building Heating Ventilation and Air Conditioning (HVAC)<br />
system via a pre-filter and other contamination control equipment. Other areas, for example the<br />
decontamination booth, will be routed via a series of High Efficiency Particulate in Air (HEPA)<br />
filters prior to the connection to the main WTB building HVAC. The airflow direction within the<br />
building will be designed to direct potential contamination away from operators towards the<br />
HVAC systems. Process layout will be optimised to ensure that handling operations are located<br />
away from access routes.<br />
The solid waste arisings will initially be collected in-situ in plastic bags. The bags will then be<br />
sealed and shipped in either 200 litre drums or other appropriate containers to the buffer areas.<br />
From the buffer areas the packages will be retrieved, transported and opened at the appropriate<br />
treatment location. These locations will include areas for segregation, sorting, shredding,<br />
decontamination, compaction and the controlled area workshop.<br />
11.2.2.1 Segregation Of <strong>Solid</strong> <strong>Waste</strong><br />
Prior to treatment by super compaction, the dry solid radioactive waste will be pre-treated to<br />
grade and size reduce large items of waste. The first step will be sorting smaller items of solid<br />
waste. This will be carried out in the sorting box. Larger items of solid waste will be collected<br />
and stored separately to facilitate easier handling of the waste. It is not anticipated that this<br />
waste will be sorted using the sorting box.<br />
Moist solid waste will be dried to prevent degradation of the waste container during storage.<br />
<strong>Solid</strong> non-compactable waste will be collected in 200 litre drums, stored in the room used for<br />
raw waste and treatment by size reduction, decontamination or dismantling in the active<br />
workshop.