ML20101G080
| ML20101G080 | |
| Person / Time | |
|---|---|
| Site: | Shoreham File:Long Island Lighting Company icon.png |
| Issue date: | 12/18/1984 |
| From: | LONG ISLAND LIGHTING CO. |
| To: | |
| Shared Package | |
| ML20101G077 | List: |
| References | |
| PROC-841218, NUDOCS 8412270420 | |
| Download: ML20101G080 (20) | |
Text
.
-. - _ ~ ~ -
n-
~
\\f i
SOLID WASTE PROCESS CONTROL PROGRAM POR SHOREHAM NUCLEAR POWER STATION - UNIT 1 REVISION O i
l LONG ISLAND LIGHTING COMPANY Docket No. 50-322 l'
December 18, 1984 Submitted By MUr 1, k, /2 [////f Reviewed By N NCko.
/4// J/d4/((
4FM/
Approved By
/c4
/4.j[Mjv rairsan,ReviewofOpe(ationsCommittee wnwaWih P
l
g- -
4 4
i
- e TABLE OF CONTENTS PACE #
1.0 -PURPOSE.........................
1 i
2.0 WASTE SOURCES......................
1 2.1 Evaporator Bottoms 2.2 Floor Drain Filter 2.3 Radwaste Filter 2.4 Spent Resin Tank 2.5 Filter Cartridges and Miscellaneous Wastes 2.6 Trash Compactor 3.0 In-House Solidification System 4
4.0 In-House Dewatering...................
4 5.0 Mo'oile Solidification and Devatering Services......
5 6.0 Solidification Process Control Parameter Determination 5
i 7.0 Solidification and Dewatering Process Control......
5 7.1 Sampling and Analysis 7.2 Conditioning 7.3 Batch Test Solidification 7.4 Waste Classification 7.5 Container Control 7.6 Decontamination 7.7 Changes to the Process Control Program 7.8 Records and Inventory Control 8.0 References 8
8.1 LILCO Operating Procedures 8.2 Mobile Services Contractor Documents 8.3 Ceneral Referknees f
Appendix A Solidification Record Sheet l
Appendix B Dewatering Record Sheet l
FIGURE 1 Solid Radwaste System A
vr-
.-w r. _ -,
^:
_=
i E
I 1.0 PURPOSE I
The Shorehan Nuclear Power Station (SNPS) Process Control Program (PCP) describes the administrative and process controls which provide reasonable assurance of a consistent quality radioactive waste product which is acceptable for shipment and burial. Implementation of this PCP will:
Provide assurance that vaste types produced at SNPS will be classified
=
satisfactorily in accordance with the requirements of 10CFR61.
1 y
Provide assurance that the requirements of 10CFR61 and specific disposal site criteria for Class A unstable waste to be solidified are met by the
]
use of a mobile solidification system supplied by a qualified contractor. When additional sample solidification data becomes available, this PCP will be modified to demonstrate the qualification of i
the in-house solidification system for processing of Class A unstable waste.
i Provide assurance that the waste form stability requirements of 10CFR61 3
q j
for Class B and C wastes are met. This will be accomplished through the
[
use of a mobile solidification system supplied by a qualified
[
contractor. Until such time as the contractor's Topical Report has been
[
approved by the h1C, qualification is based on the contractor's past
=
E record of producing acceptable BWR waste packages for vaste streams simil.
to those produced at SNPS. The contractor's Process Control Programs are referenced in Section 8.2 of this document. SNPS t
a management shall ensure that the contractor's vaste processing g
operations are performed in accordance with procedures.
g f
Provide assurance that dewatered Class A waste products meet the applicable burial site criteria for free standing water when the
. in-house or contractor's devatering equipment and procedures are used.
a 4
9 Provide assurance that the processing and packaging of solid radioactive wastes meet the requirements of federal and state regulations and i
g disposal site criteria.
t a
(
Ensure that the quality assurance requirements delineated in 10 CFR h
71.101, 71.103 and 71.105 are met for both in-house and mobile M
E contractor processing.
=
r.
2.0 VASTE SOURCES
=
L
=
2.1 EVAPORATOR BOTTOMS
=
2.1.1 Waste Evaporator
[
The Waste Evaporator receives liquid waste which is collected C
[
by ghe High Conductivity Liquid Radwaste System from floor 4
k-drains and stored in the Floor Drain Collector Tanks (FDCT).
The design output of the Waste Evaporator is an 18 weight h.
percent concentrate of dissolved and suspended solids, 2
1 tE
-1
^
^
3
s
-m
.n
- s
(
2.1.2 Regenerent Evaporator The Regenerant Evaporator receives liquid chemical wastes produced by the acid / caustic regeneration of the condensate demineraliser resins.
!The waste is collected, neutralized, and sampled in the-
~
, Regenerant Liquid and Evaporator Feed Tanks, and then pumped to the Regenerant Evaporator for concentration to a 25 weight percent mixture of sodium sulfate and other dissolved and suspended solids.
- 2.1.3 Bottoms Transfer Each evaporator is a forced circulation design with a reboiler providing process heat and an overhead entrainment separator and rectifying column which minimizes '.iquid droplets in the
- vapor. When the desired specific gravity has been reached, the concentrated evaporator bottoms are cooled and sent to the Evaporator Bottoms Tank or directly to the Evaporator Bottoms Metering Pump for solidificatien according to the contractor's
. procedure F458-P002, " Operating Procedures for Mobile-In-Container Solidification of Sodium Sulfate Slurries."
In order to provide maximum flexibility, each evaporator can be us.2d as a back-up for the other.
2.2 FLOOR DRAIN FILTER The Floor Drain Filter processes effluents from the floor and laundry drains. The filter is a horizontal traveling screen, precost type, designed for air drying and air-aided discharge of the cake'(without backflushing) into a shipping container for further devatering. The waste may'.contain filter media such as diatomaceous earth or a powdered resin / fiber blend type material.
Class A waste which is dewatered using in-house equipment is processed according to SP 23.710.02, " Dewatering of Spent Radwaste Media."
Waste which is dewatered by the contractor's mobile equipment will be processed according to references 8.2.6 or 8.2.8.
2.3 RADWASTE FILTER L.
The Radwaste Filter is used to process the following combined liquid radwaste streams:
l Low conductivity equipment drains Low conductivity wastes from the condensate demineralizer regeneration systems Ultrasonic resin cleaner backwash t
2
.n,,a,,,,..
,,,._,---,ne,--,,,-_.w.
,w--<,-,.,-
,,ma,-,,
-,,,---m,,-.,,~,-
,.-a---.
,-.r,.
,,-,<---,,-,m----,.--,
Decanted liquid from the Phase Separator and the Spent Resin Tank Blowdown from the reactor water cleanup, residual heat removal, and fuel pool cooling and cleanup systems.
The radwaste filter units are each composed of stacked horizontal filter discs assembled on an axially located hollow shaft. After draining the filter vessel and air-drying the filter cake, the filter assembly is spun to remove the filter cake from the filter discs and discharged directly into a waste shipping container for disposal.
The waete resulting from the filters may contain diatomaceous earth, Ecodex or similar powdered resin / fiber blend material. If Class A waste is being dewatered using in-house equipment, it is processed according to SP 23.710.02, " Dewatering of Spent Radwaste Media." All classes of waste may be dewatered by the contractor using procedures referenced in 8.2.6 or 8.2.8.
2.4 SPENT RESIN TANK The Spent Resin Tank accepts resin / sludge slurries (via the Phase Separator Tanks) from the reactor water cleanup (RWCU) filter demineralizers, in addition to spent bead resin from the condenrate demineralizers, the fuel peol demineralizers, and the radvaste demineralizers. The resin is allowed to settle before excess water is decanted to the waste collector tanks.
Mixed powdered and bead resin can be pumped to the Waste Devatering Tank for conditioning, followed by solidification or dewatering by in-housa equipment or the contractor's mobile unit using procedures referenced in Section 8.0 of this PCP.
2.5 FILTER CARTRIDGES AND MISCELLANEOUS WASTES Eolid wastes, such as filter cartridges from the Laundry Drain System and pump suction filters and strainers, solidification samples or other radioactive debris will be immobilized in cement which may be mixed with evaporator bottoms wastes.
Miscellaneous solids are placed within a holding device located in the approximate center of the liner and suspended off the bottom so that the cement mixture will totally surround the wastes in the basket.
Liners that contain solid objects are specifically identified.
2.6 TRASH COMPACTOR The drum compactor is used to compress low level dry waste such as rags, paper, shoe covers, floor sweepings, and plastic gloves into 55 gallon steel drums for shipment offsite. Compaction force is rated at 18,000 lbs'. for an approximate 4:1 compaction ratio.
A box compactor will be installed which compresses waste into 96 cu.
ft. metal boxes. This is a self-contained unit with its own HEPA filtering system. The compaction force is rated at 60,000 lbs.
3
4 l:.
3.0' IN-HOUSE SOLIDIFICATION SYSTEM o
.SNPS has a permanently. installed Atcor radioactive waste solidifiestion system which, when additional test data is available, will be used to:
package either radioactive evaporator bottoms or resins / sludges for disposal.as Class A waste. Until that time, all wastes for solidification
.will be transferred to the contractor's mobile equipment.
The following is a description of the in-house system. Waste and cement flows are fixed by preset metering pumps using flow rates recommended by Atcor and verified by full scale testing. Flows are also monitored by tachometers installed on the control panel. The resin / sludge is processed from the Waste Dewatering Tank and evaporator bottoms are processed from the evaporator bottoms system.
Cement and evaporator bottoms or resin / sludge are introduced into the mixer / feeder unit for thorough mixing and discharge.into a container. The small-volume continuous mixer limits the surface contact of the wet cement and also. limits the quantity of wet cement in the system at any time. A manual.handcrank is provided to permit emptying the mixer / feeder by the operator in* case of power loss or equipment malfunction.
Flush water connections are provided inside the mixer / feeder to remove cement residue.
Safety features include:
Filling cannot take place unless the fill pipe is properly inserted into the container fill opening.
An ultrasonic level sensor, and timer monitor waste level in the container to prevent overflowing. Cement-bearing flush water cannot be discharged unless a receptacle is in place.
Failure to initiate a flush sequence within 20 minutes after filling stops prompts an alarm.
The system is operated according to SP 23.713.01, " Solid Radwaste System."
A simplified functional diagram appears in Figure 1.
4.0 IN-HOUSE DEWATERING As an alternative to solidification, Class A unstable waste may be dewatered in liners which are equipped with internal cuno filters at four levels to which a pump may be attached. Pumping continues at each level from top to bottom until no additional water can be collected in an external tank.
Dewatering is e,onducted in accordance with plant procedure SP 23.710.02,
" Dewatering of Spent Radwaste Media," to assure a consistently acceptable product.
4
OQ t
. ; p _ - -. ~....~
5.0. MOBILE SOLIDIFICATION AND DEWATERING SERVICES 5.1 Wastes classified as Class B or class C must be transferred to the mobile solidification / dewatering equipment which is provided and operated by a qualified contractor. Class A dewatered wastes may be processed by the mobile services contractor at the discretio' of the l
Radwaste Engineer. Class A solidified wastes will be processed by the I
contractor until qualification of the in-house solidification system is complete.
5.2 Section 8.2 lists those procedures in use by the mobile services contractor to ensure that waste products meet all requirements for shipment and burial offsite.
5.3 The mobile equipment is installed on elevation 15' of the Radwaste Building which is a Seisade Category I structure. Spills are contained by installing the equipment in areas where sloping floors will carry liquids to floor drain sumps. The building ventilation system provides for filtering of particulate airborne contamination and monitoring of radiation before it enters the station vent.
6.0 SOLIDIFICATION PROCESS CONTROL PARAMETER DETERMINATION When additional samples have been tested for solidification, this section will contain a sutaary of qualification test results for the in-house solidification system. During the interim, the in-nouse system will not be used to solidify waste for shipment offsite.
7.0 SOLIDIFICATION AND DEWATERING PRODUCT CONTROL 7.1 SAMPLING AND ANALYSIS 7.1.1 Samples shall be obtained and' analyzed according to SP 74.002.18, "Radwa;te Sampling for Disposal," and SP 73.014.01, "Racaaste Sample Solidification Test," prior to each solidification or dewatering operation.
1.
The vaste tank to be sampled shall be recirculated for a minimum of three tank volumes prior to sampling, unless the tank has been on recirculation continuously since it began filling.
1 l
2.
The Waste Dewatering Tank is equipped with an agitator rather than a recirculating pump. Agitation is continued for at least 25 minutes prior to sampling.
3.
Funda and flat bed filter wastes must be sampled from the liner. These will not be mixed prior to sampling.
7.1.2 The waste tank sampled shall remain isolated and in recirculation or agitation, as applicable, until the solidification process is started. If it becomes necessary to add material to the tank being processed, a new batch number 5
.y will be initiated and a new sample will be taken after an appropriate mixing time.
7.1.3' Samples will be analyzed for pH and gamma emitters. ' Visual inspection will be made for oil.
7.1.4 For waste streams to be solidified, test solidifications will be performed according to the schedule described in Section 7.3.
7.1.5 Sampling. requirements apply to all waste, whether it is_being processed by permanently installed equipment or by the contractor's mobile. equipment.
7.1.6 The analysis number will be added_to the Solidification or Dewatering Record Sheet'(Section 7.8) which is prepared for each' waste container (liner or HIC). In this way the containers which belong to a particular batch can be easily identified..
+
7.2 CONDITIONING 7.2.1 Waste conditioning is required when any of the following conditions exist:
1.
A high or low pH condition, outside of the_ acceptable range according to the contractor's PCP (Section 8.2).
2.
Liquid content of the batch is above or below the acceptable envelope for solidification as indicated in Section 8.2 documents.
7.2.2 Waste conditioning will be performed in accordance with procedures referenced in Section 8.0.
7.3 BATCH TEST SOLIDIFICATION 7.3.1-Test solidification shall be performed according to the i
following schedule:
L 1.
One sample initially from each type of wet waste, and then from every tenth batch of each type of wet waste; NOTE: Batch is defined as the total volume of waste contained in a vaste mixing tank that has been L
prepared for solidification.
2.
When sample analyses fall outside the acceptchle envelope established by the mobile services contractor, indicating
, a chang. in vaste type; 3.
If it is believed that some other contaminant may be present (for example, when an unusual chemical is in use at.SNPS and may reach Radwaste).
l 6
U
-..~._.__...-m_.
.e 7.3.2 If any test' specimen fails to solidify, the solidification of the batch under test shall be suspended until such time as
-additional test specimens can be obtained,' alternative solidification parameters can be determined, and a subsequent test verifies solidification. -Solidification of the batch may then be resumed using the alternative solidification parameters.
determined.-
Representative samples shall.be obtained and tested from each consecutive batch of the same type of wet waste until at least three consecutive initial test specimens demonstrate _
solidification. The process control program shall be modified as required to assure solidification of subsequent batches of waste. The contractor shall modify his own PCP's as necessary i
to' accommodate unusual waste stresas.
7.3.3 The test specimen shall be judged to have solidified successfully if, when its container has been removed, it remains a-free standing monolith with no visible free liquid.
7.3.4 If a cement and water mixture (without vaste) is used to solidify miscellaneous objects, this mixture will be tested for e
-solidification prior to use.
i' 7.4 WASTE CLASSIFICATION 7.4.1 In compliance with 10 CFR 20.311, vastes are classified'as Class A, B or C, or greater than Class C ' based on the presence of particular radiomuclides and their activities as specified in 10 CFR 61.55. Plant procedures SP 72.713.05, " Shipment of
+
Radioactive Materisis by Exclusive Use," and SP 72.713.06,
" Calculations for Radwaste Curie Content," provide the methodology for this determination as used at SNPS.
7.4.2 Waste streams will be sampled at 6-month intervals (or more frequently, if plant parameters indicate a change in vaste characteristics) and anatyred for fission and activation products, including transuranics. Scaling factors developed from these complete analyses will be used with gamma spectra from each batch of waste to infer the concentrations of non-gamma emitting radionuclides).
7.4.3 During initial plant operation when the results of actual analyses are not yet available, generic BWR radionuclide concentrations will be taken from the Impell Corporation report entitled, " Methodologies for Classification of Low-Level Radioactive Wastes from Nuclear Power Plants."
l' 7.4.4 The curie content of waste streams (such as trash) for which E
representative sampling is difficult may be inferred based on gamma analysis of representative smears and an external dose rate measurement (SP 72.713.06).
4 i
7 i
-m
~ _ - _. _., - _ _ _. _. _. _ _ _. _.. _, _ _,, _,.., _. _ _. - - -. _ _ _,. _ _ _ _, _., _ _,
1.
ua.._..-_,.__..._..
J 7.5 CONTAINER CONTROL 17.5.1 A quality assurance program shall be established to inspect the container to be used for_ dewatering (and solidification) using SP 72.713.30, "Radwaste Container Control."
7.5.2 This program shall assure that prior to use, the containers to-be used for dewatering are intact and free of any visual damage that would prevent the dewatering of waste to required limits.
7.6 DECONTAMINATION Prior to shipment, containers will'be swiped for removable contamination and examined for general. condition. Decontamination will be conducted as necessary to meet shipping requirements.
7.7 CHANGES TO THE PROCESS CONTROL PROGRAM Any changes to the Solid West-Process Control Program for the Shoreham Nuclear Power. Station shall be approved by the Review of Operations Committee and reported to the NRC in the Semiannual Radioactive Effluent Release Report.
7.8' RECORDS AND INVENTORY CONTROL 4
7.8.1 A Solidification Record Sheet (Appendix A) shall be completed for each liner filled for solidification.
7.8.2 A Dewatering Record Sheet (Appendix B) shall be completed for each container filled with devatered waste.
7.8.3 If more than one liner results from a batch, then the initial liners will not be shipped until all liners for that batch have verified solidification. Those liners will be identified by a common analysis number (paragraph 7.1.6).
l.
7.8.4 The Solidification and Dewatering Record Sheets and the attached isotopic analysis shall be forwarded to the Radwaste Engineer for retention until such time as the liner identified on the Record Sheet,is shipped for final disposition.
7.8.5 When the identified liner is shipped, the Solidification and Dewatering Record Sheets and other documents concerning the shipment shall be forwarded to SR2 for permanent record storage.
8.0 REFERENCES
8.1 LILCO OPERATING PROCEDURES 4
8.1.1 SP 23.710.01,' Low Conductivity Liquid Radwaste
.8.1.2 SP 23.710.02, Dewatering of Spent Radwaste Media 8.1.3 SP 23.711.01, High Conductivity Liquid Radwaste 8
.. v, e
e f
?..
.8.1.4 SP 23.712.01, Regenerant Chemical Liquid Radwaste 8.1.5.'SP 23.713.01, Solid Radwaste System 8.1.6' SP 23.718.01, Liquid Radwaste Spent Resin 8.1.7 SP 23.719.01,-Liquid Radvaste Evaporator Bottona 8.1.8 SP 72.002.01, General Sampling Techniques 8.1.9. SP 72.713.01, General Requirements.for Shipping Radioactive Materials
'8.1.10 SP 72.713.02, General Packaging, Marking and Labeling-Requirements for Radioactive Materials for Shipment l
8.1.11 SP 72.713.05, Shipment of Radioactive Materials by Exclusive Use 8.1.12 SP 72.713.06, Calculations of Radwaste Curie Content.
i-8.1.13 SP.72.713.24, Sampling, Treatment and Disposal of Radioactive Waste Oil 8.1.14 SP 72.713.30 Radvaste Container Control 8.1.15 SP 72.713.35, Storage of Packaged Radwaste Liners and DAW 8.1.16 SP 74.014.01, Radwaste Sample Solidification Test 8.1.17 SP 74.002.18, Radwaste Sampling for Disposal-8.1.18 SP 78.'030.30, Lab pH Meter Standardization and Use 8.1.19 SP 73.033.10, Gamma Spectrometer System operation 8.2 MOBILE SERVICE CONTRACTOR DOCUMENTS 8.2.1 STD-R-05-007.. Topical Report, Cement Solidified Wastes to Meet the Stability Requirements of 10CFR61, Westinghouse Hittman Nuclear, Inc., April 1984.
Q.2.2 STD-R-05-005, Waste Qualification Program Report for Cement Solidified Wastes, Westinghouse Hittman Nuclear, Inc., October 25, 1983.
8.2.3 F458-P-001, Process Control Program for the In-Container Solidification of.20-25 Weight Percent Sodium Sulfate Slurries i
8.2.4 F458-P-002, Operating Procedure for Mobile Incontainer Solidification of Sodium Sulfate Slurries 8.2.5 F458-P-003, Process Control Program for Incontainer j.
Solidification of Bead Resin - Powdered Resin Mix-
.8.2.6 F458-P-004,-Dewatering Powdered Resin Slurries in Hittman HN-100 Steel Liners with a Three Layer Flexible Underdrain Assembly to Less Then 1/2% Drainable Liquid 8.2.7 F458-P-005, Dewatering Bead Resins Mixed with Powdered Resin in i
Hittman HN-100 Steel Liners with a Three Layer Flexible Underdrain Assem51y to Less Than 1/2% Drainable Liquid F458-Pg06,DewateringContainerResinSlurriesinHittman 8.2.8 9
RADl0K -100 Container with a Three Layer Flexible Underdrain Assembly to Less Than 1% Drainable Liquid 9
m..,... _. _ _. _. _. _. _ _. _ _.. _. _. _ _ _.
L. :. -.........
.. -.. = _
8.2.9 F458-P-007, Deygtering Bead Rasin Mixed with Powdered Resin in Hittman RADLOK -100 Containers with a Three Layer Flexible Underdrain Assembly to Less Than 1% Drainable Liquid 8.2.10 F458-P-008, Process Control Program for the Incontainer
)
Solidification of Powdered Resin 8.2.11 F458-P-009, Process Control Program for the Incontainer Solidification of Radwaste Filter Cake 3.2.12 F458-P-010, Operating Procedure for Mobile Incontainer Solidification of Mixed Bead Resin - Powdered Resin Slurry 8.2.13 F458-P-011, Operating Procedure for Mobile Incontainer Solidification of Powdered Resin Slurry 8.2.14 F458-P-012, Operating Procedure for Mobile Incontainer Solidification of 50% Powdered Resin /50% Diatomaceous Earth Filter Sludge 8.2.15 F458-P-013, Devatering Filter Sludge Cakes in Hittman HN-100 Steel Liners with a Three Layer Flexible Underdrain Assembly to Less than 1/2% Drainable Liquid 8.3 GENERAL "EFERENCES 8.3.1 NRC Standard Review Plan 11.4, " Solid Waste Management Systems" (NUREG-0800) 8.3.2 NRC Branch Technical Position ETSB 11-3, " Design Guidance for Solid Waste Management Systems Installed in Light-Water-Cooled Nuclear Power Reactor Plants", July 1981 8.3.3 Code af Federal Regulations, Title 10, Part 61, " Licensing Requirements for Land Disposal of Radioactive Waste" 8.3.4 Code of Federal Regulations, Title 49, " Transportation" l
8.3.5 South Carolina Department of Health and Environmental Control, i
Radioactive Material License No. 097, as amended.
8.3.6 NRC Special Nuclear Material License No. 12-13536-01, as amended, for Barnwell, SC.
8.3.7 State of Washington Radioactive Materials License fWN-1019-2, as amended, for Richland, Washington.
8.3.8 NRC Special Nuclear Material License No. 16-19204-01, as amended, for Richland, Washington.
8.3.9 ANSI /ANS-55.1/1979, American National Standard for Solid Radioactive Waste Processing System for Light Water Cooled i
Reactor Plants.
l 10 1
., _. ~.-. _
8.3.10 AIP/NESP-027, Methodologies for Classification of Low-Level Radioactive Wastes from Nuclear Power Plants, Impe11 Corporation, January 1984.
l 1
l l
l' i
11
E e
PQ WW f.7 q?
- n
.bh
',; Q. -u }{j~l'$ s!
l
~
h, 9.: u, j c:8A {jij.I$fDi IM.di :.,
li5
' F.,E Appendix A l
Page 1 of 4 SOLIDIFICATION RECORD SHEET PART I Sampling and Pre-Solidification Analysis
-1.
Type of Waste
=2.
Waste tank placed on recire.
Date/ Time 3.
Waste Tank sampled analysis IDS Date/ Time 4.
Waste Stream pH 5.
Oil Content Less than 1% (Visual Inspection)
Initials 6.
Isotopic Analysis Attached Check 7.
. Estimated Curie Concentration (SP 72.713.06) uci/cc 8.
Test Solidification Required Yes No 9.
Acceptable Test Solidification performed (if required)
Initials 10.
The above waste tank has been analyzed and is acceptable for solidification.
Radiochemistry Engineer Date or designee i
l l
.. ~.._
On O
...._y,,_.._,
,9@A (D @
$5!
r a 'hs 5; n,AQ) {;jd)' b,{A
/ ;.3 sh *
{
y,Q
/
sA
,n Appendix A Page 2 of 4 SOLIDIFICATION RECORD SHEET
,PART 11' System Preparation and Processing (Use Part iia. if-vendor supplied system is used) 1.
Container _
and (SP 72.713.30).
Type IDI
'2.
Container Properly Positioned Under Pill Pipe Check 3.
Pill Flange Properly Mated to Container _
Check 4.
Sufficient Cement Available Check 5.
Waste Dewatering Tank Level inches Evap. Bottoms Tank Level inches 6.
Authorization to commence process Radwaste Supervision Date 7.
Time process started 8.
Time process stopped-9.
. Tachometer reading (Metering Pump)
'10.
Waste Dewatering Tank Level inches 11.
Evap. Bottoms Tank Level inches 12.
Proesss Completed Operator Date Time
- 13. Waste Class:
A B
C
-14.
Liner Check for free standing water Initials Date/ Time
- 15. Liner Capp,ed Date Time 16.
Container Weight lbs.
________.___J
~
-.:.......~..--
Rm.Q. 9. TI fzC3 4.:,
a ei m.e.
m lilg..;.e
'i
.w C og.y'$j TG2) p,.i
,w, 4
L1
,4d bh bb'[4. }3 Appendix A Page 3 of 4 SOLIDIFICATION RECORD SHEET PART iia. Contractor System Preparation and Processing 1
-1.
Container ID Number Type i
2.
. Applicable connections made to liner for transferring waste and cement to liner Initials 3.
' Connections made to liner for mixing contents, if applicable Initials 4.
Process parameters 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.
Authorization to commenc.e processing Radwaste Supervision Date Time 6.
Time processing started 7.
Time processing stopped 8.
Waste Class Class A Class B Cisss C 9.
Container checked for free standing water Initials Date/ Time
- 10. Liner capped Date Time
- 11. Liner Weight lbs.
' h)4 @N9 ff:
~
d.'!
EE3-j R
41 1
8"y{,4j >;p., ',n
/.;
- a. a
- ....
t i. a 4 7 h9 3-bl 3~
~ Appendix A; I d !S !)b) ~
ij 'T h ?"
Page 4 of 4 SOLIDIFICATION RECORD SHEET PART III Filled' Liner Data 1.-
Filled Liner Radiation Levels a.
Contact Dose Rate 1 Meter Dose Rate ar/hr ar/hr b.
Smearable Activity 2
4 Quadrants 1 dpm/100 cm2 2
dpa/100 cm2 3
dpm/100 cm2 4.
dpm/100 cm
.c.
Liner decon performed
-Yes/No j
2 d.
Smearable activity.after decon (if performed) dpa/100cm e.
Liner ready for shipping or transfer to storage Health Physice Super *Tsion Date Time 2.
Storage Location Radwaste Supervision Forward this document to Radwaste Shipping Folder (per SP 72.713.01) l e
o i
4
, ~,,,. _ _ _.., _.......,,, _ _
.h Afe.s, gi" r5 3 C
i sig
.:.w;.4
.r I,
Appendix B
~*
Page 1 of 2 DEWATERING RECORD SHEET PART I Sampling and Pre-Dewatering Analysis 1.
Type of Waste 2.
Waste Tank (or Liner) Sampled
-Analysis IDI Date/ Time 3.
pH of Liquid 4.
Oil Content-(Visual Inspection)
Verify Less than 1%
Initials 5.
Isotopic Analysis Attached Check 6.
The above waste tank / container has been sampled and found to contain the isotopes and properties as indicated on the attached data sheets.
~
Radiochemistry Supervision-Date
,o P
f~
Appendix B t
Page 2 of 2 f
DEWATERING RECORD SHEET i
~PART II Dewatered Container Data
, *,'q 1,j.n
'Aj 3, cr,:}t,(;j,,,j
{'
1.
Container and l
I Type IDf
,y-g I
E4 i j
- j..... i t
2.
Container Radiation Levels O L3 6 ? > 4 u -~
a.
Contact Dose Rate Mr/hr 1 Meter Doce Rate Mr/hr b.
Smearable Activity 2
4 Quadrants 1
dps/100 cm2 2
dpm/100 cm2 3
dps/100 cm2 4
dpm/100 cm c.
Container decon performed Yes/No 2
d.
Smearable activity after washdown/decon dap/100cm e.
Liner ready for shipping or transfer to storage Health Physics Supervision Date Time 3.
Waste Class A B
C Initials 4.
Storage Location Radwaste Supervision Forward this document to Radwaste Shipping Folder (per SP 72.713.01).
- [a i, -
1 RADWASTE FILTERS FLOOR DRAIN FILTER C'OM MCTOR I
i X
[
i' o
SNSPPlate
(
CONTAIDIER SWPP1888 N
e CONTA100ER VENT ll FILTER -
SINPPMS CfMITA100ERS 1
FRoss PNASE SEPAR ATORS.
CERIENT DEWATERigge SPENT se00E
! STORAGE-l [l SILO FROM RADWASTE DEM800.
RESIN RETURN TANK CHEMICAL LINE l l ADDITION l
FROM C0000 DEBAIN. SYSTEM v
e CE T
FflOM FUEL POOL SYSTEM _
SPENT RESIN
./ V 4
ggg ER I
CEMENT SLOWER SLUDGE PUesP BATCN BIN
{-
3 WASTE DECANT p
l WATERING TO WASTE COLLECTOR TAMS
<a CEb8ENT l
j l FEEDER 9
i g
I SAMPLING g
I PU08P FROM EVAP0llATORS CEMENT 1~~~~3 ::
WASTE 1_lll wxER
[
FIGURE 1 g
"$0T0M5 E ',*"",!,"
l y
SOLID RADWASTE SYSTEM o
~
l TANK METEntNe ;PetsP lg SN990ENAbd NUCLEAR POWER STATIOff UNIT I I lC0esTAINER M SAMPLING LONG ISLAND LIGHTING COMPANY I
L1 EVAPORATOst TO MOBILE DOTTOMS SOLIDIFICATION / DEWATERING TANK PUMP
_ _ _ _ _.