29.11.2014 Views

DOE 2000. - Waste Isolation Pilot Plant - U.S. Department of Energy

DOE 2000. - Waste Isolation Pilot Plant - U.S. Department of Energy

DOE 2000. - Waste Isolation Pilot Plant - U.S. Department of Energy

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

WIPP RH PSAR <strong>DOE</strong>/WIPP-03-3174 CHAPTER 1<br />

Supporting the second and third layers <strong>of</strong> defense-in-depth, WIPP PTSR ACs are identified which<br />

establish programs for radiation protection and emergency management. Basic elements and<br />

requirements defined for TSR AC programs are enforced by the associated implementing WIPP<br />

procedures.<br />

1.3.3 Safety Analysis Conclusions<br />

1.3.3.1 Safety Analysis Overview<br />

Safety analysis was performed for the WIPP to ensure that: 1) potential hazards are systematically<br />

identified, 2) unique and representative hazards that may develop into accidents are evaluated, 3)<br />

applicable reasonable measures to eliminate, control, or mitigate the accidents are taken, and 4) safety<br />

(safety-class or safety-significant) SSCs and accident specific TSRs, based on comparison <strong>of</strong> accident<br />

consequences to the MEI to the <strong>of</strong>f-site evaluation guidelines and the immediate worker and<br />

non-involved worker to the on-site risk evaluation guidelines, are identified.<br />

The predicted RH waste (radioactive/chemical) to be received in a waste container at the WIPP was<br />

conservatively estimated based on data, as shown in the BIR 27 , from the generating sites, process<br />

knowledge, and limiting criteria provided in the RH WAC. 16 These estimates provided bounding<br />

container inventories used in the determination <strong>of</strong> potential consequences from postulated accidents.<br />

Hazards associated with the facility RH processes were evaluated through two systematic hazard analysis<br />

processes, a 72B HAZOP and a 10-160B HAZOP. The analyses encompassed waste receipt, handling<br />

and disposal <strong>of</strong> RH TRU waste in the WIPP. Each hazards analysis involved a multi-step process which<br />

included: 1) identification <strong>of</strong> the potential hazards associated with the RH TRU waste handling processes,<br />

2) characterization <strong>of</strong> the waste expected at the WIPP, and 3) a hazard evaluation in the form <strong>of</strong> a<br />

12, 13<br />

HAZOP. These multi-step processes provided comprehensive examinations <strong>of</strong> the potential hazards<br />

which may require quantitative evaluation in the accident analysis.<br />

The major hazard associated with the RH TRU waste handling process is associated with the radiological<br />

and non-radiological hazardous materials within the waste container. Hazards associated with mining<br />

operations are considered standard industrial hazards governed by OSHA and MSHA regulations and are<br />

considered only when they may be an initiating event leading to the accidental release <strong>of</strong> radiological or<br />

non-radiological hazardous materials. <strong>Waste</strong> handling operations at the WIPP do not involve high<br />

temperature and pressure systems, electromagnetic fields or the use <strong>of</strong> toxic material in large quantities<br />

outside <strong>of</strong> the waste canisters. Therefore, for the purposes <strong>of</strong> establishing an inventory <strong>of</strong> radiological<br />

and non-radiological material, only that material contained in the waste containers was considered.<br />

The hazard analysis process identified potential accident scenarios in the categories <strong>of</strong>: 1) operational<br />

accidents (caused by initiators internal to the facility), 2) natural phenomena events (e.g., earthquakes,<br />

tornadoes), and 3) external events (caused by man made initiators external to the facility). These<br />

potential accident scenarios were then qualitatively ranked in terms <strong>of</strong> consequence to the public and<br />

relative probability to determine unique and representative accidents for further quantitative analysis see<br />

Table 5.1-10.<br />

Review <strong>of</strong> the WIPP Land Management Plan 36 indicates that public access to the WIPP 16-section area<br />

up to the exclusive use area shown in Figure 5.2-1 is allowed for grazing purposes, and up to the<br />

<strong>DOE</strong> "<strong>of</strong>f limits area" for recreational purposes. The location <strong>of</strong> the MEI is at the "closest point <strong>of</strong> public<br />

access," or the <strong>DOE</strong> "exclusive use area" boundary which is consistent with guidance for the<br />

implementation <strong>of</strong> 40 CFR 191, 37 Subpart A. Calculations are performed in Appendix E for a member <strong>of</strong><br />

the public at the site boundary for reference purposes.<br />

1.3-16 January 24, 2003

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!