ML20214K046
| ML20214K046 | |
| Person / Time | |
|---|---|
| Site: | Shoreham File:Long Island Lighting Company icon.png |
| Issue date: | 11/14/1985 |
| From: | Taylor K LONG ISLAND LIGHTING CO. |
| To: | |
| Shared Package | |
| ML20214K019 | List: |
| References | |
| 4170003, PROC-851114, NUDOCS 8608150300 | |
| Download: ML20214K046 (19) | |
Text
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Document Eff. Date 11/s4/25 Rev. No.
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Prepared By Date Reviewed By Date 0' b h A &
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!! ~75~ Wm Mk' l\\lI>l8 5-APPROVALS Tit 1e/ Dept.
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IITLE OF DOCUMENT SolS l/n te freces s {c ho f hraya m l* r c
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she le. r-Power- %;,,
O nit.L COUTROLLED DOCUMENT DEC i 81985 SHOREHAM NUCLEAR POWER STATION
?0"'AEEER88888322 PDR C0"itCLLED COPY
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i SOLID WASTE PFOCESS CO! T L FPCCPJ1:
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SHOF&R: MUCITAR POER STATION - UhTT I PE'ICION 1 ITG ISIAND LIGHTING CNPKC' Docket No. 50-322 Ecvaaber 14, 1925 9
TABII OF CChT&TS PACE A 1.0 Pl>T@CSF.........................
1 2.0 VAc.TE SOUFCES......
1 2.1 Evaporator Bottcms 2.2 F3cor Drain Filter 2.3 Padwaste Filter 2.4 S p.t Resin Tank 2.5 Filter Cartridges and P.iscellt.neous Waster 2.6 Trash Ccrepactor 3.0 In-House Solidificetion Syster.
/.
4.0 In-House Dewatering...................
5 5.0 Fchile Solidification and Nwatering Sc: vices......
5 6.0 Solidificatien Process Control Parareter Deterrdration 5
7.0 Solidification and Dewatering Process Control... -,..
5 7.3 Serpling and Analysis 7.2 Conditioning 7.3 Estch Test Sclidification 7.4 Kaste Classification 7.5 Container Control 7.6 Decontarinetion 7.7 Changes to the Process Control Prograr.
7.8 Reccrds and Inventory Control 8.0 Paferences 9
B.1 LIICO Operating Procedures 6.2 Mcbile Services Contractor Docunents 8.3 General References Appendix A Solidification Pecord Sheet..........
12 W ndix B Dewatering Record Sheet...
16 FIGUFE 1 Solid Radwaste System 38 1
Page 1 of 18 1.0 PURPOSE 2e Shoreham Nuclear Power Station (STS) Process Control Progran. (PCP) describes the adninistrative and process controls which provide reasonaM e assurcnce of a consistent cuality radioactive waste product which is acceptable for shiprent and burial. Inplerrentation of this PCP will:
Provide assurance that waste types produced at SNPS wj31 be classified satisfactorily in accordance with the requirerents of 10CFP61.
Provide assurance that the reauirements of 10CFR61 and specific disposal site criteria for Class A unstable waste te be solidified are ret by the use of a mobile solidification system supplied by a qualified centractor. Khen additional sa.~ple solidification data becomes available, this PCP will be nodified to dercnstrate the qualification of the in-houre solidification system for processing of Class 7 unstablc waste.
Provide assurance that the waste form stability requirements of 10CFR61 for Class B and C wastes are met. This will be acccr.plished through tre use cf a mobile cclidificaticn syster. supplied by a qualified contractor, tttil such time as the contractor's Tepical Peport has beer.
approved by the NRC; qualificatien is based on the contracter's past record cf producing acceptable BVR waste packz.ges for waste streams similar to these produced at STS. The centractor's Process Control Progres are referenced in Section 8.2 of this document. SNPS management shall ensure that the contractor's waste processing crerations are performed in accordzrce with procedures.
Provide assurance that dewatered Class A waste products reet the applicable burial site criteria for free standing water when the in-houce or contractor's dewatering ecuirrent and procedures are ured.
Provide assurarce that the processing and pachaging cf sclid radicactive wastes neet the reqairerents of federal and state regulations and dispesal site criteria, Ensure that the quality assurance requirenents delineeted in 20 CFR 71.101, 71.103 and ~71.105 are ret for both in-house and mobile contractor processing.
2.O h7STE SOURCFS 2.1 EVAPORNIOR N E 2.1.1 K'aste Evaporator ne k~aste Evaporator receives 31gaid waste which ir ce))ected by the High Conductivity Liquid Fadwaste Syntcrr. frcra flocr drains and stcred in the T1ocr Drain Collector Tanks (TDC'T).
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Fage 2 of 1r
%e design output of the Waste Evaparator is an le weight percent concentrate of dissolved and suspended solidt.
t 2.1.2 Tegenerant Fvaporator The Pegenerant Evaporator receives Jiquid chemical wastes I
produced by the acid / caustic regeneration of the condenscte L eineralizer resins.
W e waste is collected, neutralized, and sarpled in the Fegenerant Liquid and Fveporator Feed Tanks, anc* then ptrrped to I the Regenerant Evapcrator for concentration to a 25 weight percent mixture of sodium sulfate and other dissclved and suspended solids.
2.1.3 Bottcrs Transfer Each evapcrator is a forced circulation design with a reboiler providing process heat and an everhead entrainment separator and rectifying column which minirizes liquid drcplets in the vapor. Khen the desired specific cravity has been reached, the ccncentrated evaporator bottcrs are eccled and sent to the Evaporator Bottces Tank or directly to the Evaporator Bettcrs Fetering PLrp fcr solidification according to the contractor's procedure F45P-PCO2, " Operating Procedures for bbbile In-Container Solidification of Sodium Sulfate Slurries."
i In order te provide maxir.un flexibility, each evaporater can be used as a back-up for the other.
2.2 FLOCR DBAD' FIL'IER i
The F3ccr Drain Filter processes effluents frcra the flocr and laundry drains.
We filter is a horizontal traveling screen, preccet t3pe, designed for air drying and air-aided discharge of the cake (without r
backflushing) into a shipping container for further devatering.
T'e waste ray contain filter redia such as diatcraceous earth or a powdered resin / fiber blend type material.
Class A waste which is devatered using in-hcuse equiprent is processed eccording to SP P3.710.02, " Dewatering of Spent Ra6:aste Edia."
i Waste which is dewatered by the contractor's ncbile e<pipcent will be processed acccrding to references 8.2.6 or 8.2.P.
2.3 PAN ASTE FILTER The Radwaste Filter is used to process the fc11cwing ecebined ligtau radwaste streams:
Iow conductivity equipmnt drains
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Iow ccnductivity wastes frcr. the condensate demineralizer regeneration systers Ultrasonic resin cleaner backwash Decanted liquid frcm tie Phase Separator and tle Spent Resin Ta:1 Elodown frcn the reactor water cleanup, residual heat rencycl, and fuel pool cooling and cleanup systers.
'Ihe radwaste filter units are each otrrposed of stached horizontal filter discs assembled on an axially located hollow shaft.
After draining the filter vessel and air-drying tie filter cake, the filter asserbly is spun te remove the filter cake frcrn the filter discs erf discharged directly into a waste shipping centainer for cisposal.
The saste resulting frcrn the filters rey contain diatcznacecus earth, Fcodex or similar pot.dered resin / fiber ). lend raterial. 11 Class A waste is being dettatered using in-house er3tignent, it is processed according to SP R3.710.02, " Dewatering of Spent Radwaste redia." All classes of waste ray be dewatered by ti.e contracter using procedures referenced in 8.2.6 or 8.2.8.
2.4 SPTT FISIN TAtF The Spent Pesin Tank accepts resin / sludge slurries (via the Phase Separater Tr.nks) frcr., the reacter water cleanup (PMT. ) filter decineralizers, in addition to spent bead resin f:un the condensate t'
derineralizers, the fuel pool demineralizers, and the radwaste derineralizers. The resin is allowed to settle before excess waar is dcennted to the waste collector tarJes.
Mixed podered and tecd resin can te ptmped to the Kaste Dewtering Tank for conditionirs, followed by solidification er des.atering by in-hcuse equignent or the contractor's mobile unit using procedures referenced in Section 8.0 of this ICP.
2.5 FILTER CARTRIDGES AND MIFCFIlX1G;S KASTES Solid wastes, such as filter cartridges frcr the laundry Drain ister.
and ptr p suction filters and strainers, solidification sar:ples or other radiceetive debris will be imrcbilized in cenent which ray be mixed with evaporator bottcrns t?.etes.
Fiscellaneous sclids are placed within a bolding device located in the approxirate center of the liner and sunpended off the tettm. so t'at the cen_nt rdxture will totally surround the wastes in the basket.
Liners that contain solid objects are specifically identified.
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Page 4 of 18 2.6 TPASH 00tTAC'ICR The drw crrpactor is used to ccepress low level dry waste such as rags, paper, shoe covers, floor sweepings, and plastic glover into 55 gallen steel drums fcr shiprent offsite. Corpaction force is rated at 18,000 lbs. for an approximate 4:3 ccrpaction ratio.
A box ccrpactor will be installed stich ecrpresses waste into 9C cu.
ft. metal bcxes. 'lhis is a self-contained unit with its cwn HEA filtering syster.. The ccrpaction fcree is rate' at 60,600 lbs.
3.0 IN-HOUSE SOLIDIFICATION SYSTDr SNPS has a perranently installed Atcor radioactive waste sclidificatien rytter. which, when additienal test data is available, will be used to package either radioactive evarcrator bottcns or resins /sludget fcr dis;csal as Class A waste. Until that tire, all wastes for solidification will be transferred to the centractor's rchile equi; rent.
'Ihc fc))cving is e description of the in-hcuse syster.. Waste and cemnt ficwe are fixed by preset netcring punps using flow rates rectriverdcd by Ateer end verified by full scale testing. Flows are also monitcred by tachcncters installed on the centrol panel. 'Ihe resin / sludge is processed frce. the Easte Dewatering Tank and evaporater bettcras are processed frcr.
the evaporator bottcrs syster.
Cemnt and evapcrator bottct:r or resin / sludge are introduced into the rixer/feedcr unit fcr thercugh rixing and discharge inte a centainer. The y
see.ll-voline centinuour rixer lirits the surface contact cf the wet cerent and cleo lirits the qucntity of wet cemnt in the syster at any time. A nanual handcrank is prcvided to permit aptying the rixer/ feeder by the cperatcr in case of pcuer loss or ecpirraent malfunction.
Flush water connections are prcvided inside t5e Fixer / feeder to re::cre cerent residue.
Safety features include:
Filling cannot take place unless the fill pipe is properly inserted into the containcr fill opening.
An ultresenic level sensor, and tiner nordtor waste level in tie container to prevent cverflowing. Cement-becring fluch Smter cannet Ie discharged unless a receptacle is in place.
Failure to initiate a flush sequence within 20 minutes after filling stcpc prcrpts an alann.
'nc syster is operated acccrding to SP 23.713.01, "Sclid Packaste System."
A sinplified functional diagram appears in Figure 1.
Page 5 of IC j
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40 IN-HOUSE DBGTERING As an alternative to sclidification, filter nedia may be dewatered ir.
i centainers which are equipped with internal filters to which a punp may be attached. Purping centinues at each filter until burial site criteria for free standing non corrosive liquid are net.
Dewatering is conducted in accordance with plant procedure SP R3.710.02, l
" Dewatering of Spent Radwaste Media," to assure a consistently acceptable product.
5.0 NOBIII SOLIDIFICATION ED DDaTERTNG SERVICES 5.1 Fastes classified as Class B or Class C rust be transferred to the nobile solidification / dewatering equigncnt which is previded and operated by a qualified contracter. Class A devatered wastes may be processed by the nobile services contractor at the discretion of the Padmaste Engineer. Class A solidified wastes will be processed by the centractor until qualification of the in-house solidificatien syste=~
is complete.
5.2 Section 8.2 lists these procedures in use by the rebile re2 Vices cer. tractor to ensure that waste products neet all requirements for shipent and burial offsite.
5.3 The ncbile equignent is installed on elevation 15' of the Fadwaste Building stdch is a Seismic Category I structure. Spilln are contained by installing tie equipnent in areas wtere sloping flocrs will carry liquids to floor drain strps. 'Ihe building ventilation i
syster provides for filtering of particulate airborne contamination and cenitoring of radiaticn refore it enters the station vent.
6.0 SOIIDIFICATION PROCESS CDhTROL PAPAMETEP DETEFMINATIN vhen additional scrples have been testee for solidification, this section will contain a sumary of qualification test results for the in-house so3idification systern. During the interim, the in-house system will not be used to solidify waste for shipnent offsite.
7.0 SOLIDIFICATIN AND DEGTERING PRODtLT CONTPOI.
7.1 SAMPLING AND ANALYSIS 7.1.1 Sarples shall be obtained and analyzed according to SP 74.002.16, "Radvaste Sanpling for Disposal," and SP R4.014.01, l
"Radwaste Sample Sclidificatien Test," prict to each solidification or dwatering cperation.
1.
The waste tank to be sampled shall be recirculated fer a mininum of three tank volumes prier to sarpling, unless i
Page f of 18 the tank has been on recirculation continuously since it began filling.
2.
The Kaste Dewaterdrg Tank is equipped with an agitator rather than a recirculating pmp. Agitation is centinued for at least 25 minutes prior to sampling.
3.
Funda and flat bed filter wastes nust be sampled frcr the liner. 'Itese will not be mixed prior to sanpling.
7.1.2 The waste tank sarpled shall renain isolated and in recirculation or agitation, as applicable, until the solidification process is startec'. If it beccres necesscry to add raterial tc the tank being processed, a new batch nutber will be initiated and a new sanple will he telen after an apprcpriate miring time.
7.1.3 Sa.ples will be analyzed for pH and genra emitters. Visual inspection will be rade for oil.
7.3.4 For waste streams to be solidified, test solidificationc will be perferred according to the schedule decerihed in Section 7.3.
7.1.5 Sanpling recuirs:ents apply to all waste, whether it is Ning processed by perranently installed eculpnent or by the contracter's mobile equip:ent.
7.1.6 'Ite er.alysis nurber will be added to the Solidification or Dewatering Feccrd Sheet (Section 7.8) which is prepared for each vaste container (liner or HIC). In this way the containers which belong to a particuler batch can be easily identified.
'7. 2 CC T.ITIONING 7.2.1 Waste conditioning is required when any of the following conditions exist:
1.
A high or low pH condition, cutside of the acceptr.ble range according to the contracter's PCP (Section 8.2).
2.
Liquid centent of the batch is alove or below tie acceptable envelope fer solidification as ind.icated in Section 8.2 documents.
7.2.2 Waste conditioning vill be perferred in accordance with procedures refercroed in Section 8.0.
Pagm 7 of 18 7.3 BA7Di TES7. DI.IDIFICATICN 7.3.1
'IVet solidification shall be perforned according to the fc] lowing schedule:
1.
One sample initially frcra each type of wet weste, and tien frcra every tenth batch of each type of wet waste; NOTE: Batch is defined as the total volume of waste contained in a waste rixing tent. that has been prepared for solidification.
2.
Een sample cnalyses fall outside the accep'dle envelope established by the nrbile se2 vices contracter, indicating a change in waste type; 3.
If it is believed that scrre other contarincnt rray be present (for exanp2e, when an unusual chenical is in use at S!TS and rray reach Radwaste).
7.3.2 If any test specinen fails to solidify, the solidification of the batch under test shall be suspended until such time as additional test speci2mns can be obtained, alternative sclidificatien parareters can be deterrined, and e subseque.nt test verifier solidification. Solidification of the batch rev
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then be resuned using the alternative solidificaticn paraneters detennined.
Perresentative sanples shall be ottained and tested frcr. each censecutive batch of the sa:re type of wet waste until at least three consecutive initial test specinens derenstrate solidification. %e process centrol program sFall be nodified as required to assure solidification of subsecuent batches of uncte. The certractor shall nodify hiL cwn PCF'r cs necessary to accw..u' ate unusual waste streams.
7.3.3 he test specinen shall be judged te have soliddfied successfully if, when its container has teen removed, it recins a free standing ncnolitb wit? no visible free licuid.
7.3.4 If a cerrent and water mixture (withcut waste) is ured to solidify rircellanecus objects, this rixture will be tccted fer sclidification prior tn use.
7.4 1GSTE CLASSIFICATICN 7.4.1 In ccrupliance with 10 CFR 10.311, vastes are classified as Class A, B or C, or greater than Class C, based on the presence of particular radinnuclides and their activities as specified in 10 CFR 61.55. Plant procedures SP PP.732.05, "Shi; rent of I
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Page E of 18 Radioactive Materials by Exclusive Use," and SP R2.713.0F, l
" Calculations for Padwaste Curie Content," provide the i
rnethcdology for this determination as used at SNPS.
j 7.4.2 Waste strears will be surpled at (-conth intervals (or rcre frequentJy, if plant parereters indicate a change in wa.nte characteristics) and analyzed for fission and activation products, including transuranics. Fealing factors developed frcn these ccrplete analyses will be used with gamt rpectra frco each batch of waste to infer the concentrations of non garrra erritting radionuclides).
7.4.3 During initial plant operation when the results of actual analyses are nct yet avai]al-le, gereric EXh radicnuclide concentrations will te taken frcar. the Inpel) Corporation repcrt entitled, "Nethodologies for Classification of Ice-IcVel Radioactive Wastes frca Nuclear Pcrer Plants."
7.4.4 The curie content of waste strears (such as trash) for which representative sanpling is difficult nry be inferred based en game analysis of representative smears and an external dose rate measure: rent (SP R2.713.06).
l 7.5 COhTAINEP.CCtimOL 7.5.1 A quality assurance program shall be established to inspect the container to be used for dewatering (and solidification) using SF R2.713.30, "Padwaste Container Control."
l 7.5.2 This progran. shall assure that prior to use, the certainers to be used for dewatering are intact ard free of any visual damage that wculd prevent the dewatering of waste to regaired limits.
7.6 DECONTAMDG.TICt; Prior to shipDent, containers will he PViped for rerrvable contamination and exarined for general condition. Decontarinatien will be conducted as necessary to neet shippino requirercents.
7.7 O?ANGES 'IO 'n:E PROCESS CCNIROL PROGPM:
Any changes to the Solid Waste Process Control Prograr. fcr the Shoreham Nuclear Power Station shall be approved by the Review of Operations ccmr.ittee and reported tc the hTC in the Serrlarrual Padioactive Effluent Release Poport.
7.8 PICORDS AND DNENTOPY CaTROL 7.8.1 A Sclidification Reccrd Sheet (Aptendix A) shall be ccrpleted for each liner filled fer so3361fication.
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Page 9 of 18 7.8.2 A Dwatering Pecord Sheet (Appendix E) shall be capleted fcr each container filled with dwatered waste.
7.8.3 If wre than one liner results frcrn a batch, then the initial lincrs will net be shipped until all liters for that batch have verified solidification. 7 hose linerr will be identified by a comon analysis nurrber (paragraph 7.1.6).
7.8.4 he Solidification and Dewatering Record Sheets and the attached isotopic analysis shall be fonearded to the Pa&aste Engineer fer retention until such tire as the liner identified on the Record Sheet is shipped for final dispositicn.
7.0.5 Kher the identified liner is shippal, the Sc>1ir:3 ficatien and Dwatering Pecord Sheets and otrer documents concerning the shiprent shall be forwarded to SP2 fcr pentanent record stcrage.
8.O REFERENCES 8.1 LIICO OPERATING PRCCEDI'RES P.1.1 SP R3.710.01, low Conductivity Licuid Radwaste 8.1.2 SP R3.710.02, Dewatering of Spent Radwaste Eeiia I
8.1.3 SP 23.711.01, High Conductivity Liquid Padwaste 8.1.4 SP 23.712.01, Pegenerant Chemical Liquid Radwaste 8.1.5 SP 23.713.01, Solid Padwaste Systar.
L, 8.1.6 SP 23.718.01, Liquid Fadwaste Spent Resin 8.1.7 SP 23.719.01, Liquid Padweste Evaporator Botters 8.1.8 SP 72.002.01, General Sa g ling Techniques 8.1.9 SP PS.713.01, Shiprent of Padioactive Paterials 8.1.10 SP RB.713.02, General Packaging, Pzrking and Iabeling l
Pecyirenents fcr Pzdioactive Faterials fer Shiprent E.1.11 SP PE.713.05, Shipenent of Radioactive Fateria]E by Exclusive l
Use S.1.12 SP R2.713.06, Calculations of Radwaste Curie Centent.
8.1.13 SP R2.713.24, Sarpling, Treatncnt and Dispesal of Radicactive Faste Cil 8.1.14 SP P2.713.30, Radwaste Container Control S.I.15 SP P2.713.35, Storage of Peckaged Fadwe.ste Liners and DAW E.1.16 SP R4.014.01, Radwaste Sarple Solidificction Test 8.1.17 SP 74.002.IE, Pedwaste Sanpling for Disposal P.I.18 SP 78.030.30, Lab pH Feter Standt.rdiretien and Use 8.1.19 SP 73.033.30, Ganra Spcctrcreter System Operation P.2 POPILE SEWICE COhTIGC70R DOCUMENIS 8.2.2 S7B-P-05-007, Epical Peport, Genent Solidified Westes to Feet the Stability Pequirerrents of 10CFRC), Westirghcuse Hittran Nuclear, Inc., April 19C4.
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Page 10 of IR 8.2.2 STD-R-05-005, Waste cualification Progre Peport for cement Solidified Kastes, Westinghouse Hitten Neclear, Inc., October 25, 1983.
P.2.3 F456-F-001, Process Centrol Prceram for the In-Container Solidification of 20-25 Weight Percent Scdium Sulfate Slurries S.2.4 F458-P-002, Operating Procedure for Mobile Incontainer Solidification of Sodium Sulfate Slurries-S.2.5 F458-P-003, Process Centrol Program for Inccntainer Sclidification of Bead Resin - Iowdered Pesin Fix E.2.6 F45P-F-004, Devatering Povdered Resin Slurries in Eittman HN-100 Steel Liners with a 'lhree layer Flexible Underdrain Asserbly to less Then 1/2t Drainable Liquid 8.2.7 F458-P-CC5, Dwatering Bead FesinF Mixed with Powdered Pesin in Fittnn hW-100 Steel liners with a 'Ihree layer Flexible Underdrain Assebly to less 'Ihan 1/2% Drainable Liquid E.2.8 F458-Pg'C6, Dewatering Container Besin Slurries in Eittnan EADIIE -100 Container with a Three Iayer Flexible Underdrain Asserbly to Iess 'ihan 1% Drainahle Lic,uid 8.2.9 F/.56-P-007, Deg.tering Eez.d Resin Miyed with Powdered Racin in Hittman RADIIE -100 Containers with a 'Ihree layer Flexible Underdrain Asseb]y to less 'Ihan it Drainable I.1 quid 8.2.10 F456-P-008, Process Control Program for the Incontainer Solidificaticn of Powdered Resin B.2.11 F458-P-009, ProcesF Control Progra for the Incentainer Solidification of Radwaste Filter Cete 6.2.12 F458-P-010, Cperating Procedure for tbbile Incentainer Solidification of Mixed Bead Eesin - Powdered Pesin Slurry E.2.13 F.M8-P-011, Operating Procedure for Nobile Incontainer Solidification of Powdered Resin Slurry P.2.14 F45E-P-012, Operating Procedure for Mobile Incontainer Solidification of 50% Powdered Pesin/50% Diatmaceous EaI+J1 Filter Sludge 8.2.15 F458-P-013, Devatering Filter Sludge Cakes in Mittman FF-IfT Fteel Liners with a 'Ihree layer Flexible Underdrain Assently to Iess than 1/2% Drainable Liquid
Page 11 of IE 6.3 GE12VJ. REFEPD'CES 8.3.3 NPC Standard Review Plan 31.4, "Sclid Waste Managc cnt Systers"
(??UREC-0800) 0.3.2 NPC Branch Technical Position PTSB 11-3, " resign Guidance for Felid hste Managerent Systeurs Installed in Light-Water-Cooled Nuclear Power Ecactor Plants", July 19El 6.3.3 Chie of Federal Regulations, Title 30, Part C2, " Licensing Fequirements for Iznd Disposal of Radioactive Waste" 8.3.4 Code of Federal Regulaticns, Title /9, "Transportatien" 8.3.5 Scuth Carolina Departrent of Health and Environmental Contrcl, Eadioactive Material License Eo. 097, as ananded.
L.3.6 NRC Special Nuclear Eaterial License No. 12-13536-01, as ancnded, for Em. ell, SC.
6.3.7 State cf Washington Radioactive mterials License an'-ICC9-2, as anended, for Richland, Washington.
E.3.0 f.TC Special Nuclear Paterial License Nc. 16-19204-01, as anerded, for Richland, Washington.
8.3.9 AMSI/M:S-55.1/1979, Arterican National Standard for Solid Padioactive Waste Processing System for Light Water Cocled Reacter Plants.
8.3.10 AIF/NESP-027, Methodologies for Classification of Irv-I(vel Padioactive Wastes frce Nuclear Powe.r Plants, Inpell Ccrperation, January 19F4 l
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Page 12 of 18 Appendix A Page 1 of 4 SOLIDIFICATION RECDRD SHEET PART I Sampling and Pre-Solidification Analysis 1.
Type of Waste 2.
Waste tank placed on recire.
Late / Time 3.
Waste h nk sampled analysis ID#
Date/ Time 4.
Waste Stream pH 5.
Oil Content Iess than it (Vin:a1 Inqu: tion)
Initials 6.
Isotopic Analysis Attached Check 7.
Esti! rated Curie Concentration (SP R2.713.06) uci/cc l
8.
Test Solidification Rapired Yes No 9.
Acceptable Test Solidification performed (if regaired)
Initials
- 10. W e abcve waste tank has been analyzed and is acceptable fer EOlidificatiCn.
Padiccheristry Enginee'r' Date or designee 1
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Page 13 of 18 APPendu A Page 2 of 4 SOLIDIFICATION RKORD SHEET PAPT II Systen Preparation and Processing (Use Part iia. if vendor supplied syste is used) 1.
Container and (SP P2.713.30).
l Type ID*
2.
Container Properly Positioned Under Fill Pipe,,_
Check 3.
Fill Flarge Properly Pzted to Container Check 4.
Sufficient Cerent Available Check 5.
Waste Dewatering Tenk Ievel inches Evap. Bettms Tank level inches 6.
Authorization to cmrence process Radwaste' Supervision
'Date Y
7.
Tire process started 8.
'Iime process stopped 9.
Tachmeter reading (Metering PLmp)
- 10. Waste Dewatering Tank Ievel inches
- 11. Evap. Bottms Tank Ievel inches
- 12. Process Ca pleted Operetor Dete Tire
- 13. Et.ste Class:
A B
C
- 14. Liner Check for free standing water Initials Date/ Time
- 15. Liner Carped,,
Date Time
- 16. Container Weight lbs.
1.
.,s
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Page 14 of 18 l
Appendix A Page 3 of 4 SOLIDIFICATICN RECORD SHEET PART iia Centractor Syster: Preparation and Processing 1.
Container ID Nurber Type 2.
Applicable connections made to liner for transferring waste and cerent to liner Initials 3.
Connections made to liner for mixing contents, if applicable Initials 4.
Process parcmeters Waste to be added to liner cu. ft.
Cement to be added to liner cu. ft.
Water to be added to liner cu. ft.
5.
Authcrization to carnence processing RadwasteSupervision Date Time
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Time processing started i
7.
Time processing stepped 8.
Waste Class Class A Class B Class C 9.
Container checked for free standing water Initials Date/ Tire
- 10. Liner capped,
Date Time
- 13. Liner Weight lbs.
1.
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Page 15 of 18 Appendix 7 Page 4 of 4 SOLIDIFICATION RDCORD SHEET
'AM III Filled Liner Data F
1.
Tilled Liner Radiation Ievels a.
Contact Dose Rate 1 Meter Dose Rate mr/hr Inr/hr b.
Stearable Activity 4 Quadrants I dp/100 2
dyr./100 3
dp/100 an2 4
d p/100 an c.
Liner decon perfomed Yes/?b d.
Streart.ble activity after decon (if perfomed) dp/IO0an e.
Liner ready for shipping er transfer to storage Health Physics" Supervision Date Tue 2.
Storage Ircation t'
Radwaste Supervision Fcrward this document to Radwaste Shipping Folder (per SP RS.713.01) l i
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Page 16 of IE Append 2x B Page I cf 2 DD7TEP.ING R*: CORD SFTfr PART I Sanpling and 7talysis 1.
Type of Waste 2.
Warte 'Iank (or I.iner) Sampled Analysic IDf Date/ Time 3.
Oil Content (Visual Inspection)
Verify Imss than it InitfaTs-4.
Isotopic Arilysis Attached creck 5.
'Ibe above waste tank / container har, beer sant ed and found to contain l
the isotopos and properties as indicated on t?m attached data sheets.
Fi3Icichmistry Supervisiori Iiete t'
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a n...
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Page 17 of 18 Appendix B Page 2 of 2 DDATERING REDRD SHEET PAF.T II Dewatered Container Data 1.
Container and Type IDt 2.
Container Radiation Irvels a.
Contact Dose Rate Mr/hr 1 Meter Dose Rate Mr/hr b.
Srcereble Activity 2
4 Cuadrants I
dpr/ICO at 2
dpr./100 3
dpn/100 cr7 4
dpa/100 on c.
Centainer dccon performed Yes/lb d.
Shct.rable activity after washdcyn/decon dr.p/10ra.'
e.
Liner ready for shi g ing or transfer to stcrage liealth Physics Supervision Date Tire
'(
3.
Fastc Class A B
C Initials 4.
Storage locatien
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hacivarte Supervisicn Forward this docurent to Radt.? rte Fhipping Folder (per SP PR.713.01).
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