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RADTRAD Design, As Built,

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LOCA, requires multiple cases (containment release, ESF release, and multiple X/Q paths) ... and release files to allow LOCA-ESF, MSLB, SGTR's to be run ... – PowerPoint PPT presentation

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Title: RADTRAD Design, As Built,


1
RADTRAD Design, As Built, Updates
  • Terry Heames
  • ALION Science and Technology
  • presented at the
  • NRR AST Workshop
  • 22 June 2006

2
Outline
  • RADTRAD Design
  • As Built
  • Current Errors
  • Modifications

3
RADTRAD Design
  • The 1994 model designed to do
  • Use NUREG Spray and Natural Deposition models
    (Powers, Henry, or User)
  • Overlying pool decontamination (Powers)
  • Iodine re-evolution (ORNL)
  • Filter decontamination (User)
  • Transport (use but not derive flows)
  • Onsite Offsite dose analysis
  • NUREG 1465 and TID 14844 source terms
  • It had numerical problems

4
RADTRAD Design Reg Guide 1.183 1.195
  • The 2002 release (3.03) designed to perform
  • Spray and natural deposition decontamination
  • Filter decontamination
  • Transport
  • Onsite Offsite dose analysis
  • Correct known errors
  • Follow the guidance in RG 1.183 1.195
  • Provide reliable answers

5
RADTRAD 3.03 As Built
  • The 2002 version (3.03) was not designed to
    perform
  • Iodine re-volatilization (pool)
  • Pool pH versus time analysis
  • Appendix I (Equipment Qualification)
  • Filter failure and re-entrainment
  • Decay of deposited isotopes
  • AEB 98-03 steam line deposition or release

6
RADTRAD 3.03 As Built
  • The 2002 version (3.03) was not designed to
    perform the guidance efficiently
  • LOCA, requires multiple cases (containment
    release, ESF release, and multiple X/Q paths).
    Steam line deposition, spray decontamination
    limits all offline.
  • FHA, CRDA, LRA acceptable
  • MSLB SGTR inventories available in Ci/cc or
    Ci/hr translate to Ci/MWt
  • Nobles and Alkali Metals inventories 100/Ebar

7
RADTRAD Error Notices
  • 12 Error Notices since 6/2002
  • First 5 were found between the release of 3.03 by
    ITSC and the release by the NRC.
  • The NRC version has all these modifications.

8
RADTRAD Error Notices
  • 7 Control Room X/Q Time Intervals Ignored
    (7/04)
  • 8 Powers Natural Deposition Model chooses
    PWR (10/04)
  • 9 10 Compartments generates source term
    errors (10/04)
  • 10 Inaccurate activities when decay of
    nuclides with lt 2 hr half lives. (12/04)

9
RADTRAD Error Notices
  • 11 Source term compartment without initial
    Iodine doesnt decay Tellurium correctly. (1/05)
  • 12 Powers Natural Deposition inaccurate.
    (2/05)
  • 13 Abrupt Flow Changes in Time causes dose
    inaccuracies. (3/05)

10
RADTRAD 3.10 Modifications
  • 3.10 allows path dependent X/Qs, to allow
    variation with release point and/or intake
  • 3.10 allows use of a multi-bin/multi-volume,
    homogeneous, or slug deposition model MSIV
  • 3.10 allows spray DF limits
  • 3.10 decay and daughtering of deposited nuclides

11
RADTRAD 3.10 Modifications
  • 3.10 allows multiple inventory and release files
    to allow LOCA-ESF, MSLB, SGTRs to be run as
    single cases
  • 3.10 edits activity (Ci) of airborne deposited
    nuclides in both compartments and paths.
  • 3.10 edits exposure (Ci-hr) and decays of
    airborne nuclides for shielding and pH calcs.

12
RADTRAD 3.10 Still Missing
  • Average Beta and Gamma energies (base for pH,
    shine, and 100/Ebar analysis)
  • Qualified Main Steam deposition model
  • Re-entrainment model
  • SI units for I/O

13
  •             Other than pain in generating the
    100/Ebar limit for non-iodines in the coolant,
    has anyone ever seen that it made a difference in
    the dose?  If not why add to the pile of
    information in a submittal?
  •  
  •             In one of the RAIs the NRC requested
    that the submittal use the total iodine released
    over the total amount currently in the atmosphere
    as the basis for a DF limit because it will
    decrease the time the sprays are on.  Are there
    calculations to show that this is important?  If
    one uses the correct definition of DF, i.e. the
    amount in the atmosphere the amount deposited
    over the amount in the air, the difference
    between the 2 definitions is at best less than a
    few minutes.  Why a concern?
  •  
  •             I know you do not like to go to far
    from where the data is but one of the submittals
    used a pool height of 19 for the computing the
    DF in a FHA.  The complaint was the basis point
    (i.e the DF at 23) but not the use of the
    approximation at such a low depth.  What is the
    level that is acceptable?
  •  
  •             There was a complaint about a
    shielding calculation where one set of pipes
    passed behind another and there was some space
    for additional shine to get through in the
    spaces.  Unless this is a particularly high
    activity situation, arent you worrying about
    small lt1 effects?

14
Main Steam Line
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