ML102180372
| ML102180372 | |
| Person / Time | |
|---|---|
| Site: | Humboldt Bay |
| Issue date: | 07/29/2010 |
| From: | NRC/FSME |
| To: | |
| References | |
| Download: ML102180372 (40) | |
Text
Humboldt Bay Power Plant NRC presentation July 29, 2010 Agenda" Introductions and purpose of this meeting* H BPP Site Orientation" Alternate Disposal Method Request(s)" Reactor Vessel Transportation and Disposal" DCGL's and LTP HBPP Site* 2 Operating Steam Generation Fossil Units 9 2 backu pGas Turbines* Operating ISFSI* Construction of New Generation Facility* Unit 3 Nuclear Plant decommissioning
- Preparation for Units 1 and decommissioning 2
Alternate Disposal Request" Purpose of the Alternate Disposal Request (submitted April 1, 2010)* Schedule of Units 1/2 decommissioning" Proposed answers to questions on submittal" Travel Route from Eureka CA to Grand View Idaho (HBPP to USEI)" Weather or road re-routing of trucks" Potential future alternative disposal request(s)
Potential Alternate Disposal Requests* Open air demo limits established at HBPP Unit 3 will require concrete shaving* Resulting concrete structures will be very low concentration limits, consistent with current request* Soils concentrations of SNM very localized* Potential that an additional 1000 shipments will meet current alternate disposal concentration criteria Potential Alternate Disposal Requests e State of Calif Department of Toxic Substances Control (DTSC) clean up standards are based on combined cancer risk model, rather than a dose based model* Increase total shipments c
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Stp In UwP DLDveomn* Pefr a sorc ter abtacin le Develo an epsur scenaio Deie a mtemaia moe base on*Syrgooia knowledgeS Deive sigl nucid soi 5 3\Deiv sigl nucid stutrlufc pCL/S and Deiv soi an sufc Sre factors Stp to Sorc Ter Absrcto Inopoae pas 10 C1caatrzainrsls0n Thortia rdoules narw dt02H I ieseii poeta rainclds" Ra ionu lids wihh l-ie < .4y as( h lfiv )wer exldd xep o o6" ~ Lo -eaieaudnerdincie icutd n"~ ~ ~ 0aual ocurn raincie0nisigihbefo bakron weeecldd Sorc Ter Abtaton ot Chrcerzto sape wer colce for- -~anlyi of poeta radionSuclies SImace are soi samples" Cocrt core to idntf dept ofpntrto an voum aciainprdcs n"~~~ Cocrt SOSbl sa pe tidnfysufc contamination.
S Onl 2 ra in cie eeid niidi@ol I Half Life (Years)Decay Mode Half Life (Years)Decay Mode Radionuclide Radionuclide Am-241 4.32E+02 a, y 1-129 1.57E+07 V3-, y C-14 5.73E+03 Nb-94 2.03E+04 3-, 'y Cm-243 2.91E+01 a, y Ni-59 7.50E+04 F Cm-244 1.81E+01 a, 7 Ni-63 1.OOE+02 Cm-245 8.50E+03 a,y Np-237 2.14E+06 aqy Cm-246 4.75E+03 aq, Pu-238 8.78E+01 a, y Co-60 5.27E+00 13-, y Pu-239 2.4 1E+04 a, y Cs-137 3.02E+01 Pu-240 6.60E+03 a, Y Eu-152 1.36E+01 f3-, y Pu-241 1.44E+01 Eu-154 8.80E+00 J3,, y Sr-90 2. 86E+O1 3-H-3 1.23E+O I Tc-99 2.13E+05 P-,rY Sorc Ter Absrcin Cot Dos modlin objetive Deive sigl nucid DCI onl fo detecte radiouclids, an Acon fo no-etce Ssite-specific poental raincie when comparSingto anu a dos limit
- ~ Al 143 ace r m atdicuig 0 105RP r 2liesdIF I
Sceari Develpet Cot Log-er PG& exetto to manti sit fo 0 lcria generation0 and trnmsin 0 and PG& ined torti it wesi thrug 0h foeeal future0 00 -0 .0 14 Scenario Development, Cont..Industrial worker scenario chosen for use with RESRAD for soil DCGL derivation:
RESRAD chosen because of subsurface soil contamination, Industrial worker is most appropriate scenario for foreseeable future, and Dose contribution due to detected soil radionuclides indistinguishable from background after 100 years.
Scenan'o Development, Cont Alternative critical groups and exposure scenarios have been considered:
A resident farmer establishes occupancy after release of site from Industrial Area use, and If the site license is terminated at uniform industrial worker scenario DCGLs, the site is in compliance with the regulatory limit 32 years later using a resident farmer scenario.
Sceari Deeopet Cont BUID* Tieost eulydvie@ewe inor S n outdoors.
5 ~ -SSS .55 *7
-pl m0 a -.1jnato of S :;i 0CG-.*E A 6 wa chse to deiv soi*C w due SoS th prsec of subsurface solcnaiain
-SE A caclain wer pefre in th prba iisi 0oe Derivation of Soil DCGLs, Cont.A RESRAD simplified mathematical hydrogeological model was derived based on existing knowledge-" Site studies define soil and aquifer profiles from surface to potable water aquifer," Approximately 400 ft from surface to potable water aquifer, Several clay layers exist between surface and potable water aquifer, and Brackish water aquifers exist above the clay layers.
Peak Dose at 1 pCi/g (mrem/vrl Nuclide DCGL (DCi/gl AM-241 1 .76E-02 1 .42E+03 C-14 4.98E-06 5.02E+06 Cm-243 7.78E-02 3.21E+02 Cm-244 6.82E-03 3.67E+03 Cm-245 5.44E-02 4.60E+02 Cm-246 1 .26E-02 1 .98E+03 Co-60 1.64E+00 1.52E+01 Cs-137 3.79E-01 6.60E+01 Eu-152 7.40E-01 3.38E+01 Eu-1S4 7.97E-01 3.14E+01 H1-3 8.66E-06 2.89E+06 1-129 1.95E-03 1.28E+04 Nb-94 1.09E+00 2.29E+01 Ni-59 6.05E-07 4.13E+07 Ni-63 1 .65E-06 1 .52E+07 Npm-237 1.31E-01 1.91E+02 Pu-238 1.09E-02 2.29E+03 Pu-239 1.21E-02 2.07E+03 Pu-240 1.21E-02 2.07E+03 PU-241 4.11 E-04 6.08E+04 Sr-90 3.1OE-03 8.06E+03 I ol 1 ,
isRSA-UL 33ue in, probabilisti mode an DCL, auesbsdoSninutilwre bildn ocuac scenari introdced i S SOS S675. -U 5-in 21 i i Dose Conversion Factor (mrem/vr Der dnm/100 cm 2)Radionuclide DCGL (dDm/100 cm 2)H-3 6.07E-07 4.12E+07 C-14 2.05&-05 1.22E+06 Ni-59 3.09E-07.
8.09E+07 Co-60 1 .54E-03 1 .62E+04 Ni-63 8.08F,07 3.09E+07 Sr-90 2.01E-04 1.25E+05 Nb-94 1.06E-03 2.36E+04 Tc-99 2.08E-06 1.20E+07 1-129 2.74E-03 9.12E+03 Cs- 137 4.44E-04 5.63E+04 Eu-152 7.57E-04 3.30E+04 Eu-154 8.26E-04 3.03E+04 Np-237 5.28E-02 4.73E+02 Pu-238 7.01E-03 3,57E+03 Pu-239 S. I7E-03 3.06E+03 Pu-240 7.26E-03 3.44E+03 Pu-241 1.38E-04 1.81E+05 Ani-241 8.34E-03 3.OOE+03 Cm-243 5.20E-03 4.81E+03 Cm-244 3.97E-03 6.30E+03 Cm-245 8.60E-03 2.88E+03 Cm-246 2.08F_,-02 1.20E+03 Deiaino ddtoa CLa In ad ito to thi soil an surfac areas, 0~ were alo evloe for-I-Thic soils,0 Vouercmtras Em ededpiin, n Buie pipng Area Factor = DCGLEMc DCGLW metodg of S- 5 , and Humboldt Bay RPV Project NRC Update 7/-29/2010 Reactor Pressure Vessel Project Goal* Package and Transport HBPP Reactor vessel as an single component package as an LSA shipment in a DOT IP2 package Plant History.65 MW GE Boiling Water Reactor m Approx 5E 5 years effective run life m.Reactor last run in 1976 with approx 35 years of radioactive decay Initial Characterization" Performed in mid 1990s by TLG to support cost estimate for decommissioning" Activation analysis for characterization was performed on internals and vessel* This results in conservative estimates of the part 61 classification of activated internals Current Approach* Normalize the prior activation analysis by dose rate" Determine final classification of vessel based on total activity averaged over metal volume in accordance with the BTP* Perform partial segmentation of internals to remove items to meet the 1R at 3 meter unshielded dose limit Regulatory Basis of Approach m 10 CFR 71.14 concerning transport of LSA materials* NRC Branch Technical Position (BTP) on Concentration Averaging 1995 Segmentation discussion Classification
-Remove internal components to meet 10CFR61 classification as a Class A package-Remove additional internal components to meet the 1R at 3 meter limit of 10CFR71. 14 ALARA Basis for Approach* Segment GTCC waste and place in ISFSI" Segment B/C waste and store on-site until disposal option becomes available" Reduce dose consequence-to workers by minimizing segmentation of internals" Reduce Radiological risk in transportation by minimizing truck quantities of less stable packaging alternatives Project Schedule m Selected RPV removal contractor June 2010.7.* Complete RPV characterization Oct 2010" Mobilize for site work March 2011* Ship reactor vessel February 2012 Summary* Minimum segmentation to do.is the ALARA thing m Making a single disposal package is the ALARA thing to do.* The single package results in safety to the public.