ML19224B290
| ML19224B290 | |
| Person / Time | |
|---|---|
| Site: | Crane |
| Issue date: | 07/03/1974 |
| From: | Metropolitan Edison Co |
| To: | Mullinix W NRC/IE |
| References | |
| 1629, TM-0411, TM-411, NUDOCS 7906140402 | |
| Download: ML19224B290 (10) | |
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'DfI DOCUMENTS (Al' O//H DOCuuEter NO:
79061404ot COPY MADE ON OF DOCUMENT PROVIDED BY METROPOLITAN EDISON COMPANY I!M4A Wilda R. Mullinix, NRC 7906140$90E
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UNIT #1 HEALTH PHYSICS PROCEDURE 1629 Liquid Waste Disposal System "ampling. (Pertinent to OP 1104-2.9-A-W)_..
Table of Effective Pages Page Date Revision Pa_g e, Date_
Revision Page Date
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'/ 1629 Revision 0 2
THREE MILE ISLAND NUCLEAR STATION 2/8/74 HEALTH PHYSICS PROCEDURE 1629 Liquid Uaste Disposal System Sampling 1.0 FURPOSE This procedure describes the samples that must be taken of various radioactive liquids prior to utilizing the liquid in another opera-tion or prior to transferring the liquid to other components of the liquid waste disposal system (pertinent to OP llc 4-29-A through Y).
2.0 DISCUSSION The liquid waste disposal system has been engineered to maintain radioactivity levels in liquids at or below designated values.
The major components of the system are tanks, pumps, pre-coat filters, demineralizers, evaporators, coolers, and ficor and equipment drains with associated sumps.
The liquid waste disposal system provides oper-ating service functions to the primary system and spent fuel pools in addition to the collect on, containment and processing of miscellan-ecus wastes for re-use or disposal. The functions are as follows :
2.1 Operating service functions to primary system and spent fuel pools.
2.1.1 Chemical shim and volume control for primary system.
2.1.2 Pressurizer relief suppression, containment and collection.
2.1.3 Drain and fill primary system.
2.1.4 Clean-up spent fuel pool water.
2.1.5 Process primary coolant and refueling water for re-use er f
4 disposal.
2.1.6 Process spent fuel pool water for re-use er disposal.
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1629 Revision 0 2/8/74
'2.2 Miscellaneous Tunctions of the LWDS:
2.2.1 Process miscellaneous wastes from:
2.2.1.1 Radioactive laberatory drains, 2.2.1.2 Building and equipment drains, 2.2.1.3 Regeneration of deborating resins,
2.2.1.4 Discharge of spent resins from demineralizers,
2.2.1.5 Discharge of used pree r o from preccat filters, 2.2.2 Process radioactive laundry and shower drain waste for disposal.
2.2.3 Safely dispose waste liquids from both functions to the river.
2.3 The amount of a adicactivity in the liquid is dependent on the use of that liquid at the nuclear station.
Primary coolant is expected to have higher radioactivity levels than water used in the laundry of contaminated clothes.
It follows that speci-fications as to the acceptable level of radicactivity in liquids to be used for one purpose will differ considerably from those used for another purpose.
In crder to verify the radioactivity level in a liquid, samples are take and analyzed for gross beta-gamma activity.
The liquids are then treated by filtration, -
demineralization and/cr evaporation, as required.
2.4 Liquid waste disposal system piping is so arranged that all liquids collected in equipment of either *ae primary coolant or miscellaneous waste chains must be routed through the reactor coolant or miscellaneous waste evaporators and the con-densate demineralizers and be collected in the waste evacorator
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condensate storage tanks before they can be discharged to the mechanical draft cooling tcwers.
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3.0 REFERENCES
3.1 FSAR Vol. 4 3.2 FSAR Vol. 5 3.3 OP-1104-29 A thru Y, Liquid Waste Disposal System 3.4 10CFR20 3.5 10CFR50 3.6 OP-1104-43, Nuclear Plant Sampling 3.7 PCP 1950, Determination of Tritium, PCP 1929, Determination of Solids, Suspendeo and Dissolved, PCP 1912, Determination of Boron, PCP 1900, Determination of pH, PCP 1901, Determination of Conductivity.
3.8 SP 1301-6.3, Condensate Storage Tank 4.0 EQUIPMENT 4.1 End= window G-M detector 4.2 GeLi detection system 4.3 Sampling container 5.0 OPERATING INSTRUCTIONS 5.1 Liquid radioactive samples will be collected either in the Nuclear Sampling Room (elevation 305') or locally.
Proce-dures for collecting samples from the Nuclear Sampling Room are found in OP-1104-43 Nuclear Plant Sampling. Those samplee collected in the Nuclear Sampling room are:
5.1.1 Cation demineralizer "B" cutlet 5.1.2 Cation demineralicer "B" inlet 5.1.3 Cation demineralizer "A" inlet 5.1.4 Cation demineralizer "A" outlet
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5.1.5 Miscellaneous Waste Storage Tank 5.1.6 Reactor Coolant Bl6ed Tanks 3.0
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1629 Revision 0 2/8/74 5.1.7 Laundry Uaste Storage Tank 5.1.8 Deborating Demineraliser inlet 5.1.9 Purificating Demineralizer outlet 5.1.10 Make-up tank 5.1.11 C. H. Cooler outlet 5.2 The local samples to be taken are as follows:
Neutralicer waste storage, feed and mixing tanks; Reclaimed Boric Acid Tank; R. C. Vaste Evape;rator; Concentrated Vaste Storage Tank; Spent Resin Storage Tank; Used Precoat Tank 5.2.1 Neutralizer Waste Storage and Teed Tanks.
S.2.1.1 The three-tank conplex involved in neutra]
lithium hydroxide and flush solutions used to regene resins of the Deborating Demineralizers is used for this purpose 2 or 3 times within an approximate two conths span at the end of a core lifetime. However, the functions of the neutralizer system have been expanded to include storag capacity for emergency transfers from the miscellaneous
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Waste Storage Tank (UDL-T2) and the Laundry Waste Storage Tank (WDL-T12), and the capability to neutralize, or add anti fcan agent to, miscellaneous and laundry wastes prior to their evaporation in the miscellaneous waste evaporator.
5.2.1.2 If the Neutralizer Teed Tank was essentially empty when a a
new batch of waste was transferred into it and if an adequate sample and analysis for the new batch are available, the new batch does not have to be resampled before transfer to the 197 097 u.0
.1629
.Tevision 0
-I 2/8/74 neutraliser mixing tank for processing.
However, if the
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neutralizer feed tank was not empty when the new batch was transferred into it or if the sample analysis for the new batch does not have the necessary information, the new batch shall be resampled and analyzed before transfer to the neutralizer mixing t3- : for processing.
5.2.1.3 The aaalysis on the pre-neutralization samples shall include a gross beta-gamma activity determination. This determination shall be made in accordance with PCP 1950.
5.2.1.4 The sample from the reed Tank is obtained locally by closing valves WDL-V150 and WDL-V154, WDL-V144 & WDL-V148 and start pump WDL-P9A.
Recirculate the liquids for 1 hour1.157407e-5 days <br />2.777778e-4 hours <br />1.653439e-6 weeks <br />3.805e-7 months <br /> prior to taking sample.
5.2.1.4.1 Open WDL-Vl90 and purge sample line a minimum of three (3) sample container volumes.
5.2.1.4.2 Collect an appropriate sample.
5.2.1.4.3 After sample has been collected close UDL-Vl90.
5.2.1.4.4 Stop pump WDL-P9A.
5.2.1.4.5 Open valves WDL-V154 and WDL-V150, 'ciDL-V144 and '.TDL-V148.
5.2.1.4.6 Flush sample lines per step 5.2.1.6.1 thru 5.2.1.6.4 5.2.1.5 Samples are obtained from the ::eutraliser Waste Storage Tank by llosing valves ' TL-V150, WDL-V144, WDL-V146 :nd WDL-V153.
5.2.1.5.1 Start pump WDL-F3A and allow centents to rec..rculate for one hour prior to collecting sample.
5.2.1.5.2 Open valve WDL-V191 and purge sample line a minimum of three (3)
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4 sample container volunes.
5.2.1.5.3 Collect an appropriate sample.
5.2.1.5.4 After sample has been collected close WDL-Vl91.
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1629 Revision 0 2/8/74 5.2.1.5.5 Stop pump WDL-P9A and open valves WDL-V153, WDL-V150, WDL-V144 and WDL-V146. s 5.2.1.6 After samples have been taken, valves returnec'. to normal and pumps stop, purge appropriate sample line(s) as follows: 5.2.1.6.1 Close valves WDL-V153 and NDL-V154 5.2.1.6.2 Open valves WDL-V316, WDL-V190, WDL-V317, UDL-Vl91. Allow reclaimed water to clear the sampling lines for 5 ninutes. 5.2.1.6.3 Close valves WDL-V316, WDL-V317, WDL-Vl90 and NDL-Vl91. 5.2.1.6.4 Open valves WDL-V154 and WDL-V153. 5.2.2 Reclaimed Boric Acid Tank 5.2.2.1 Each batch of reclaimed boric acid from the Reclaimed Boric Acid Tanks shall be sampled and analyzed prior to transfer to the concentrated Waste Storage Tanks, to the Reactor Coolant Evaporator Peed Tank, or to the Miscellaneous Waste Evaporator Feed Tank. Analysis shall include a gross beta-glama activity determination acccrding to PCP 1950, 5.2.2.2 Close valves WDL-V49, JDL-V91, WDL-V94 and WDL-V96. Activate pump WDL-P13A and allow fluid in WDL-T7A to recirculate one hour prior to collecting cample. 5.2.2.3 Cpen valve WDL-V193 and purge sample line a r.inimum of three (3) sample container volumes. 5.2.2.4 Collect an appropriate sample. 5.2.2.5 After collection of sample close valve WDL-Vl93. 5.2.2.6 Stop pump UDL-P13A and open valves WDL-V96, WDL-V91, WDL-V94 k. and WDL-V49. 5.2.2.7 Tcr sampling solution in Reclaimed Beric Acid Tank WDL-T73 close valves WJL-V49, WDL-V89, UDL-V94 and WDL-V95. Activate pump UDL-P13A and recirculate one hcur prior to collecting sample. 197 099 ~
1629 Revision 0 ~' 2/8/74 5.2.2.8 Open valve WDL-Vl93 and collect sample. ~ 5.2.2.9 After collection of sample close 7alve WDL-Vl93. 5.2.2.10 Stop pump WDL-P13A and open valves '.!DL-V95, WDL-V89, WDL-V 1 and WDL-V49, 5.2.2.11 Purge the sampling line by opening valves WDL-V319 and WDL-Vl93. 5.2.2.12 Close valves WDL-V319 and WDL-Vl93. 5.2.3 Prior to transferring concentrated wastes from the Concentrated Waste Storage Tanks to the Miscellaneous Waste Evaporator Feed Tark a sample must be taken and analyzed for dissolved solids concentration, gross beta-ganma activity level and boron content. (See PCP's 1929, 1950 and 1912.) 5.2.3.1 Gross beta-gamma activity will be determined according to PCP 1950, 5.2.3.2 The sample will be gathered locally. To sample concentrated waste storage tank WDL-T6A cicsc valves WDL-V331, WDL-V104, WDL-V243 and WDL-V106. 5.2.3.3 Start pump WDL-P12A and allow concentrated wastes en WDL-TGA to recirculate for one hour prior to sampling. 5.2.3.4 Open valve WDL-Vl94 and purge sample line a minimum of three (3) sampls container volumes. 5.2.3.5 Collect z.n appropriate sample. 5.2.3.6 After samp2e has been ecliected close WDL-V194 5.2.3.7 Stop pump WDL-P12A and cpen valves WDL-V106, WDL-V243, WDL-VIC4 and WDL-V331. 5.2.3.8 Sampling frca Concentrated Waste Storage Tank WDL-TEB can be [. 4 realized by closing valves WJL-V102, WDL-V106, WDL-V243 and WDL-V332. S.2.3.9 Start pump WDL-P12A and allow contents of WDL-T63 to recir-culate for one hour prior to sanpling. 7.0 l-
,1623 Revision 0 [ 2/8/74 I 5.2.3.10 Collect an appropriate sample by opening valve WDL-Vl95 and purge sample line a minimum of three (3) sxnple container volumes before sample is collected. 5.2.3.11 Close valve WDL-Vl95 after sample has been collected. 5.2.3.12 Start pump WDL-P12A and open valves WDL-V332, WDL-V243, WDL-V106 and WDL-V102. 5.2.4 Spent Resin Storage Tank 5.2.4.1 Liquids to be decanted frem the spent resin storage tank shall be sampled and analy cd for conductivity, gross beta-gamma activity and pH. 5.2.4.2 Cross beta-gamma activity will be determined according to PCP 1950. 5.2.4.3 Close valves from used pre-coat tank (WDL-V143, WDL-V142, WDL-V141, WDL-V140 and WDL-V139). Also close valves WDL-V195, WDL-V234 and WDL-V235. 5.2.4.4 Activate pump WDL-P10, 5.2.4.5 Cpen valve WDL-V196 and purge sample line a minimum of three (3) sample container volumes. 5.2.4.6 Collect an appropriate sample. 5.2.4.7 After collection of sample close valve WDL-Vl96 and stop pump WDL-P10. 5.2.4.8 Open valves WDL-V23 5, WDL-V2 34, WDL-V18 5, WDL-V13 3, WDL-V140, WDL-V141, WDL-V142 and WDL-V14?. 5.2.5 Used Precoat Tank 5.2.5.1 Each batch of liquid waste to be decanted from the used pre-coat t ank will be sampled and analyzed for grcss beta-gamma j activity. This determination will be acccmplished eccording to PCP-1950. 5.2.5.2 Close valves frca the spent resin storage tank (WDL-V134, WDL-V135, WDL-V136,.DL-V137, and WDL-V133). Aqspplos 3.0 l-
1629 Kevision 0 2/9/74 valves WDL-V234, WDL-V235 and WDL-V184 5.2.5.3 Start decant pump WDL-P10. 5.2.5.4 Open valve WDL-Vl97 and purge sample line a minimum of three (3) sample container volumes. 5.2.5.5 Collect an appropriate cample. 5.2.5.6 After collection of sample close valve WDL-V197. 5.2.5.7 Stop pump WDL-P10. 5.2.5.8 Open valves WDL-V184, WDL-V235, WDL-V234, UDL-V138, WDL-V137, WDL-V136, WDL-V135 and WDL-V134, 5.2.C Waste Evaporator Condensate Starace Tanks 5.2.6.1 Contents of the waste evaporator condensate storage tanks will be sampled prior to their release from the tanks and as specified in SP 1301-6.3. 5.2.6.2 In order to sample contents of waste evaporator condensate storage tank WDL-T-llA close the following valves; WDL-V121 WDL-V125 WDL-V131 WDL-V123 WDL-V126 WDL V128 5.2.6.3 Start pump WDL-P148A.
- 5. 2. f. 4 Allow contents to recirculate for 1 hour.
5.2.6.5 Open valve WDL-V200 to collect sample. 5.2.6.6 Close valve WDL-V200 af ter sample has been collected. 5.2.6.7 Stop pump WDL-P14B. 5.2.6.8 Open the following valves: WDL-V128 WD L-V126 4 4 WDL-V123 WDL-V131 WDL-V125 WDL-V121 5.2.6.9 Rinse sampling line by opening valve WDL-7337 and UDL-V2CO. Close valves UDL-V337 and WDL-V200 after a few mi ,0L7 1 i 9.0 h
-a rv..,_an 0 2/8/74 .'~ .4 :, ~., - 5.2.6.10 In order to sample contents of waste evaporator condensate storage tank WDL-T-llB close the following valves: WDL-V119 WDL-V130 WDL-V125 WDL-V126 WDL-V123 WDL-V129 5.2.6.11 Start pump WDL-P14B. 5.2.6.12 Allow contents to recirculate for 1 hour. 5.2.6.1; Open valve WDL-V201 to collect sample. 5.2.6.14 Close valve WDL-V201 after sample has been collected. S.2.6.16 Open the following valves: WDL-V129 WDL-V130 WDL-V126 WDL-V125 WDL-V123 WDL-V129 5.2.6.17 Rinse sampling line by opening valves WDL-V339 and WDL-V201. Close valves WDL-V338 and WDL-V201 after a few minutes. ae e 10.0 5}}