ML20059J184
| ML20059J184 | |
| Person / Time | |
|---|---|
| Site: | Farley  |
| Issue date: | 08/24/1990 |
| From: | ALABAMA POWER CO. |
| To: | |
| Shared Package | |
| ML20059J168 | List: |
| References | |
| FNP--M-11, FNP-0-M-011, NUDOCS 9009190206 | |
| Download: ML20059J184 (99) | |
Text
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July 12, 1990 i A Revision 10
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JOSEPH M. FARLEY NUCLEAR PLANT FNP-0-M-011 1 m o s-
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- OFF-SITE DOSE CALWTION 'ANUAL
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( ' Technic ~al (Manaoe E ' Date Issued:' [-1 $ VYM - List of Effective Pages Page , -Rev. i o . 1,ii,iii,1v,v,1-2,2-1 to 2-16,3-1 to-3-5, . . 10 j 3-17,3-18,3-21,3-22,3-24 to 3-30,3-50,5-2.to 5-4,6-1, 10
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3-19 '8 . l 1-1,3-6 to 3-16,3-20,3-23,. .7-3-31 to 3-49,4-1,54,5-5 to 5-7,6-2 to 6-9
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Appendir 10 I 4 ObCM-2 . i
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.l CONTENTS , I j
.s. PAGE: TABLE OF CONTENTS i j , LIST OF TABLES. 11 -
. LIST OF FIGURES 111
-1 1
OOCM4ECHNICAL SPECIFICAT!'N CROSS REFERENCE TABLE , iv_
. REFERENCES V-- -l CHAPTER 1l INTRODUCTIONS 'l .
. -- 4 i
CHAPTER 2 LIQUID EFFLUENTS , , 1
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4.1 LIQUID-RELEASE CONFIGURATIONS '. .. . .c. .- . . = . . '2-1 1 2.2 SETPOINT CALCULATIONS -..:. -
.;1.-.-..'.'. . . . 2 1 2.3'
~
' 10CFR20 AND TECHNICAL SPECIFICATION COMPLIANCE -. .!2-71 l' 2.* DOSE CALCULATIONS. . . .... -
. .. ....s. . . 2-8 2.5 COMPOSITE ANALYSESI... . . - .; . .... . . , .... .-. .~2-11s 2.6 DOSE PROJECTIONS . . . ... .
. .1. .
...7 .. .- . . 2-11' CHAP 1ER 3 ! GASEOUS EFFLUENTS- 1 3 3.1 GASEOUS' RELEASE CONFIGURATION ..a :.-.-. . .-.>. 3 '
3.2 CALCULATIONS.OFlX/Q AND D/Q VALUES . . . . . . . .;3-4 3.3 SETPOINTS FOR GASEOUSL MONITORS ! .- .. . . . .... . ..3-171 3.4 3 GASEOUS 10CFR20 COMPLIANCE . .'. .-1... .-. . .-,'3-21: ' 3.5 GAS WASTE S'IORAGE TANK . . . . .,. . ... . .
.. . . 3 3.6 CUMULATIVE DOSE CALCULATIONS .
c........ .n. . 3L25 3.6.1 Dose Calculations rom Noble = Gas ' Releases ; ... . 3-25f 3.6.2 -.d Dose Calculations For. Radionuclides In Particulate Form . . . . . . . . . . . . c . . - . - 3a 7 ) 3.7 COMPOSITE ~ ANALYSES . . . . : . : . . . . . . . . . . . > :> 0 H l' 3.8 DOSE PROJECTIONS . . . . . . . . . ... . ... . .J3-50 t , i l-t< h CHAPTER 4 TOTAL DOSE . ; 4-1~ 3 CHAPTER 5 RADIOLOGICAL ENVIRONMENTAT MONITORING . LOCATIONS 5-1 CHAPTER 6 METEOROLOGICAL
SUMMARY
- 6-1 - t
. APPENDIX ODCM EQUATIONS AND SOURCES A-1 t
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N. 1 .
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l; } List of Tables- l
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~Page 1
- 2-1 Liquid Release Tanks and Mca.itor:; ' '2-1 t 2-2 Bioaccumulation Factors '2-12 4 2-31 JIngestion Dose Conversion Factors- 2-13 ,
I 2-4; Liquid Effluent Dose Commitaent Factors'. '2-15
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3-1 Gaseous Release Sources, Release' 3-2.
. Points, and Monitors 1
3-2 Site Boundary and Limiting rood- , 3-7 Pathway Distances- i 3 ' Dose Factors for Noble Gases.and .3 Daughters-3-4 ' Infant Dose Factors 3-24' 3-5 Organ Dost Factors'for Each Nuclide ;3-31 5-1 RadiologicallEnvironmental Monitoring; 5-2. y. s Q, Locations , y 6-1 .X M Values for Mixed Mode 6-2
' 9' 6-2 XM Values for Ground Level Releases 4; a
6-3 DM Values for Mixed Mode 6-6' ' 6-4 .D/Q Values for Ground Level Releases $-8_ . , 1
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; Listiof Figures- ,
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'2 . Liquid waste' Release Tanks' 2-2 i-l 2-2' . Routine Liquid Waste Effluent, Pathways 2-3 3-1 Gaseous Release Sources 3-3 ,
y 1r E , 3-2' vertical Standard Deviation of the' Plume 3-8 4 y 3-3 Recirculation Factor . . . 3-9 -
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3-4 Ground. Level.' Relative Deposition .3-131 7; 3-51 : Elevated Relative > Deposition -130 m 3-14 _ 3 -Elevated Relative. Deposition i6b m' 3-15. '
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7 Elevated ; Relative Deposition.-- 100 m'. 3-16 , 5-1 Airborne Sampling Locations Lat Farley .- '5-5
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Nuclear Plant,'0-5000 feet' , 1 2 vi
' Airborne Sampling Locations at Farley; 5-6.- l
. Nuclear Plant, 0-20 miles 5-3 Water Sampling Locations ~for Farley;. 5-7 .
1 Nuclear Plant' 1,
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ODCM-TECHNICAL SPECIFICATIONS' CROSS REFERENCE TABLE -! l I _ Radiological Effluent Technical Specification
. Dose Calculation
( j ODCM L Section- -Methodology: '
.Page'
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3.3.3.10. ' Determination of 2-4 : Alarm Trip Setpoints' For Liquid. Monitors- i ' 3.3.3.11 Determination of- 3-17 l Alarm Trip Setpoints ~ For Gaseous Monitors 4
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4.11.1.1.li
-Lii;[uid Effluents - 2-71 4 .11'.1'.1. 2 Liquid Effluents 2-7 c ]
4.11.1.1.3 Liquid Effluents i t
-4.11.1.2 Liquid Effluents' '2-8.
4'11.1.3.1-Liquid Effluentsj< 2-11' i 4.11.2.1.1 Noble Gases ;3-21' e
,1 4.11.2.1.2' Gaseous Effluents 3 ' m a
4.11.2.2 0 Noble Gases 3-251 ' I 4.11.2.3 .Radiciodines and. 3-27 j! Radioactive Materials' in-Particulate Form- < 4.11.2.4.1 Gaseous Effluents: 3-50 4 i 4.11.4 Dose Assessment:for' 4-l' - Environmental-Radiationi
-Standards 4.12.1 Radiological 5 Environ--' 5.-1 ; J -
. mental Monitoring. i 6.9.1.9 :I ODCM All 6.9.1.10 ODCM '
-All j 6.14 ODCM
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REFERENCES '
.i h 1. Boegli~, J.S', R.R. Bellamy, W.L.-Britz, and R'.L. Waterfield, L , " Preparation - of Radiological Effluent .Technica)
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. -Specifications 'for -Nuclear Power Plants,' "NUREG-0133' ,t (October 1978). ,,
- 2. Methods for Estimating Atmospheric Transport and Dispersion i' of Gaseous Effluents in Routine Releases from'. Light.- Hater -
Cooled- Reactors, U.S. NRC ' Regulatory . Guide ' 1.111j- (March, 1976). ' 3.- Methods for Estimating'At "ansport and: Dispersion.-
-of Gaseous Effluents in Roy < , es-from Light - Water -:
Cooled- Reactors, U. S . ~ NRC fegulatory Guide 1.111,- Revc_1; a j (July, 1977). 4.- Calculation of Annual Doses to Man: frr.n Routine Releases of. Reactor Effluents for the 0Purp7se cf JEvaluating' ComplianceL 1 j with 10CFR Part 50, Appendix I . U.S. - NRC L Regulatory l Guide /- 1.109, Rev. 1 (October 1977).
- 5. Plume Rise, G. A. Briggs, U.f. fAtomicc Energy.. Commisioni '
Critical Review Series, TID-25073,~1969. #
- 6. Meteorology - and Atomic En<srgy, David H.- Slade,: editor,c Technical Information 1 Centrs t, <U.S. . Department l' of / energy, 1968. __
1 y
- 7. T. E.. Young, . T. S. _Bohn, and W. Serrano, -"Technisal.;
Evaluation : Report for the- Evaluation of ODCM LRevision A7 ' + Joseph M. Farley Nuclear Plant,: Units.l.and 2",l EGG-PHY.8674 i dated August 1989, transmitted.by.NRC' letter dated 11-9-89..
- 8. - Jackson,' W. II M., " Survey-Report of Chattahoocheeo River Water 1 Use Downstream of Farley: Nuclear . Plant Liquid " Effluent d L Discharge", dated July 19, 1990.. 1
- 9. " Calculation' of, Annual Doses. to Man from Routine Releases 'of ,
Reactor Effluents for the' Purposes of; Evaluating : Compliance - with '10 CFR 50, Appendix I".,. U. S. NRCURegulatory Guidei i 1.109;. Draft, March 1976.
'i
- 10. Kocher, D. C., " Radioactive. Decay Data Tables",
DOE / TIC-11026, dated 1981. y 11'. Joseph M. Farley Nuclear Plant Environmental' Report Operating License Stage (July'28, 1975). . f n t v '-Rev. 10 -H l 1 [~ . L L li n ,- ..- . . - - . . . . - s+ , , , , , -
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- i I CHAPTE:R 1 .
1 i
-INTRODUCTIONi
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This'Off-Site Dose Calculation Manual (ODCM)' describes the' methods'- if used at Farley Nuclear Plant (FNP) for: complying with the effluent ,' release! portions ' of the FNP . Technical Specifications and the < requirements ' of 10CFR20)and Appendix I ~ of l10CFR50, w The concentration and dose, limits: that are required to be met-and ' r which are described. in this manual 'are:: 4-u
- o' For; radioactive lliquidEeffluents, Lthe concentrations- <
released _to areas beyondithe' site boundary are' limited to the values given in 10CFR20, Appendix'B, Table II., , o- For radioactive liquid affluents, the maximum ~ dose to any member of the public will'be less than the lirits given in
.10CFR50, Appendix!I. -
~o For gaseous ' effluentsi ' the J dose o rate : at any ilocation - {
beyond the : site boundary :will be ; limited tot the3 annualc ' dose limits.given in:10CTR20. ' o For gaseous effluents, <the . maximum dose toiany member s of
~
j the public will'be'less than<the limits tiven in 10CFR50, ' Appendix I'. , o The - maximum dose to; any member - of1 the public will .. not-exceed the limits given in 40CFR190-The equatiopsf employed are taken ' from NUREG-0133f'and; Regulatory Guide l'.111 .~- References to Regulatory l Guides are give. .with the equation- numbers' in this ODCM.' . , Dose fa r or taken directly froa Regulatory. Guide- 1.109,ctors' are calculated - s ,, l
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'FNP-0-M-Oll This 00CM describes the physical configuration of release sources <
and release points for routine and non-routine liquid and1 gaseous effluents, the monitor setpoint calculations, dose, and dose rate calculations.: Units 1 and 2 have independent release points for gaseous releases, and . a common release point for liquids'. For ' gaseous ' releases,1 dose limits for, the, site are : normally apportioned-equally . between ._ - the : two units, ' independent of the . operational . status of either: unit but may be altered .to allow more dose appropriation to either unit as necessary.= i i
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CHAPTER 2 LIQUID ErrLUENTS { 2.1 LICUID RELEASE CONFIGURATIONS l Routine uliquid releases for each unit are discharged through a single release point. These are normally-batch releases from the controlled discharge of liquid waste tanks. 'A simplified; diagram of the' waste tanks and the discherge paths is'shown-in rigure 2-1., Radiation monitor-RE-18Lis on the discharge' path. Routine releases are normally. batch or continuous releases'of the.- we.ste sources listed in Table 2-1E i Table 2-1. Liquid Waste Effluent Pathway 4 for Routine Releases: , Tank Release g Volume Monitor *-
.i Wast'e Monitor Tankil batch .5000 gal; 1/2 RE18i Waste Monitor Tank 2. batch 5000 gal 1/2 RE18 Turbine Building continuous or batch -- - - '
Sump > l Steam Ger.erator continuous -- 1/2 RE23A, Blowdown 1/2 RE23B-h i Figure 2-2 shows the relationship of all of.the routine liquid- i effluent pathways and the combined discharge:to-the river. -i Oth9r be potential effluent pathways are monitored regularly,-and may ~I treated as non-routine releases,.- if required. iNon-routine a releases are un-monitored during release. Dose he ' made based on estimates of :; the. activity calculations.willl concentration i'and~ j .. : valume'of flow released. '
*1/2 stands for Unit 1 or Unit 2 k
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Tux 2 . . TANK 1 STRUCTURE .'l
' WASTE I REUSE d' 8v'P05^T0" -- ~"' ' '
CONDINSAT1
- TANK - ' d= '
4 Figure 2-1.. Liquid Waste ReleasecTanks 1/2 018- l 2-2 Rev. 10-l= i 0-L _- - _ _ = - - - - - - - - - - - - - - - - - - - - - - - - - " " --- - '
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. Liquid Effluents.
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. ,i Unit I- , Undt'2 1- '
i Service Water , Service. Water;,, q I? Train A- Train B. LTrain'A :TrainsBi- i H i I d - Cooling Tower Blowdown '7 *
.i 4 _Radwaste Discharge- *
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. 1RE018' -2RE018 1 4 Steam Generator Blowdown; y IRE 23B ,
f2RE23B . i
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To River l 1 s l l 31 Figure 2-2. Routine Liquid Waste Effluent Pathways 2-3 Rev..J10 l l L n'
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., , i Liquid Effluents ~
2.2= SETPOItfr CALCUIATIONS Calculations ~are made for the' radiation'. monitors to determine the alarnVtrip setpoints. so that 10CFR20' compliance is _ met? for the-effluent pathway. atithe site boundary; These - : calculations;use- ,
' the maximum permissible concentrations-(MPC) from-10CFR20 Appendix'- 3 B,- Table 1II, . Column. 2,'. and the'. more conservative of : the ~ soluble ~
- (S) totalorofinsoluble;LpCi/mlLis.used.<(I).
2 x 10' values except for.'the noble gases for whicho 1 ne relationship that must be met to ensure'10CFR20' compliance is. . C ' E. f 1: (2.1). >
- 1. 'MPCg - ,
=where N
C, , , = ; concentration" of radionuclideli J at '- the site 0 boundary: -
- 1
-(discharge structure at the. river) in vCi/m1'.:. a ' -
=
MPC, "10CFR20 - Appendix ' B, Table- . II; Column "2 values except ' for ' inoble gases. j I= Sum over'all=radionuclidesc , g 4.- The concentration at, the" site -boundary includes? theLcont'ribut' ion-from all sources of- both Units 1 and 2' .- hetvalue'of C.; -
- calculated value' since only; the Econcentratcd 2 input 'stre& Ins.eis a-iare- '
measured for radionuclide content.: Therefore :'. 2' I ' C' ' " ' '
- f" ' "
1 C,,= g I , f( 2 '. 2 ) . u=1 ! F, d where '
, C,,,,, -
concentration of :radionuclide',' i , -- in the . effluent. pathway, p, from Unit, u,Lin'vCi/ml. f, , , =
~
flow rate from the effluent pathway,: p,: from the Unit, ~u, ,9 in gpo. F, = ; dilution flow (service water a'd ncooling tower.: blowdown) plus I f,,, in gpm. - j P q
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Liquid Effluents, ,! x , , i 3 Each unit has an established and measured dilution flow so that if W Ct ,u
- g. <1 ,
3 )n .L' LMPC( is net for each unit then _ equation 2.1~ will bMd. for- the site,
- where'C 1 is . the ' concentration of radionucir. ,11,- in the - '
aist:harg6"from Unit- u.' -
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Thus- the unit specifis 10CFR20 limit can;be fonnulated as' - 1 E C 1', u , p :
- i fu , p P
g > 7"- ' ' i . f1 '
-(2.3) '
MPCi--- Toaccountformultipleeffluentpathwaysfromasinyle'iunit.an. > apportionment factor, Ar,, will be defined for each pathway such~.
-that 1 C , , , ,
- f, , ,
i g p"
'<- 'I g
i
-< AFu ,p
- .(2.4)\. < !
l. o with the restriction that ' hs- , P I AF, , p $1 - (2' 5) _ l '
-Rearrangingiequation 2.4 and substituting Dm ,p>for 0
.-.u-F atithe 6
u
,ulp- s limit of the: inequality then_
~
1~ Dg , , = I
'C**" -i i
AF,,, i MPCi -(2;6)f : l whereDgI4thwaytomeet10CFR20limitsat-thesiteboundary-is effluent _ the mini
-(assumes all the pathways ~at the maximum value).
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'A-safetyfactor.of'211snowapplied[tocompensatefor uncertainties in the measurements and calibrations'so.that the. 1 required dilution factor (Dr o ,,) is ;
- Dr, , , = 2
- Dm, , , -(2.7) and can~be calculated for-each effluent. pathway;using. ,
=
2 C ,,,, 3 Dr" I ,
' .AF, , , = MPC. :(2.8)-
L Iflthe required dilution facfor;is'l'ess;than 1, dilution is not' ) required, but a'setpoint must still.be calculated.
- To allow the discharge to occur.without reaching the monitor ,
setpoint the actual, or anticipated, dilution factor (Da- -- be; greater than'the required dilution factor, Dr . Thlk')-must' requirement will limit the effluent release poinl'Ilow rats.'.The- . monitor setpointyis defined as' ' i
%,,= (Da,,, - Dr,3) I C (2.9).
f; g,,,, Dr, , 7 i
~ where i Mu ,, = setpoint in ci/ml, f I
i- C"'" = Sum over all gama.-emitting: radionuclides /in. the . undiluted waste'~ stream (the.monitorLis sensitive only 4 toi gama-rays) . ? in=which i 1 Dr,,3 = - u,p H3
'1 and 1
2
- C*'"
Dr" ' ' = I
-l AF, , , i MPC g
*Alliradionuclides except H3.
'J
. .Cg16"e'Iorthewastestream.'is va greater than or equal to the previous monthly composite l L once the setpoint has been established the releaseLpathway j
'flowrate must be controlled to less than or equal to the maximum- '
value, F,/Da,,,. l^ 2-6 Rev. 10 l v l v ,
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'MP-0-M-011 Liquid' Effluents-
<j For1the-setpoint in counts pet tinut'e (cpm)
SPC p .=E,*.4[,+B,,, (2.10) l where E, = monitor calibration factori(cpnV Ci/ml);
^
B,,,'= effluent monitor backgrourid in' epm For a potential' effluent pathway, e.g. the service. water, that has-
^
no detectable activity,.the setpoint should be set as close to background as practical ~_to alarm if;an inadvertent' release were to occur but prevent spurious ~ alarms. The monitor setpoints determined in accordance with.the~ ! methodology described-above establish the upper > bound for-a-
- particular monitor setpoint. Monitor'setpoints'may be established: i at lower values-if desired.
2.3 10CTR20 AND TECHNICAL SPECIFICATION COMPLIANCE 2.3.1 Prior to Release 1 Prior to releaise,,all tanks to belreleased is'a; batch are isolated from the source-and recirculated a minimum ~of two- d volumes to ensure adequate. mixing. The oatch tank (is'then sampled after the appropriate mixing.- Recirculation time' 1 to ensure adequate mixing is calculated as follows:1 -! minimum recire duration (minutes): == tank content (gallons)'x 2 l recire rate (gpm) : Prior ~to making a. discharge the following parameters-are- 3' established for the release: 1
- a. Monitor.setpont (if.the pathway has a' monitor). .
J,
- b. Maximum effluent pathway release flow, rate.
- c. Anticipated dilution-flow rate. i
- d. Assurance that the condition of equation (2.3) will be met considering all effluent pathways during the D discharge.
l 2-7 Rev. 10 i 4
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< FNP-0-M-Oll'-
Liquid Effitents-
.i
.-2. 3. 2 During the Release !
During the:releas'e the following informationishould be. l l- recorded:: r L a.- Actual flow race of the effluent. release pathway, t
- b. Actual dilution-flow rate.
- c. ; Effluent monitor response 1 (if there is an-operable effluent monitor in the release pathway)~. ~
2.3.3 After the Release-After the celease is conpleted, the ' actual effluent .
' discharge ji. formation recorded during.the release is used l to verify that the-condition of equation (2.3) was met j
. during the' discharge where f,3 and' F, are the ' actual flows ;
recorded. ' s 2.4 DOSE CALCULATIONS t
.A river use. survey was conducted'(reference 8) on the !
chattahocchee. River and Lake Seminole below Plant Farley. The
. survey encompassed' drinking water, irrigation of crop and gardens,~
fishing, and recreational use of the river and shoreline. Only , two pathways,to: man for the uptake:of the liquid. effluents were-identified. These are fishing:andsirris tion.and-consumption a of '
)
vegetables. . Therefore, the dose; calculations will consider fish; Lt and green leafy vegetables irrigated with river water consumed by'.' an' adult as the maximally exposed individual ~.- ' J
- L The dose limits.specified inLTechnical Specification 3.ll;1.2'.are on a per reactor. basis. Therefore=the doses calculated in this:
subsection .will be on a per reactor-basis. 4 The dose-to the: maximum exposed' individual due to radionuclides ' l identified in each liquid. effluent release L from each unit:to unrestricted areas will'be calculated as follows:. ., 'i s D, = [ [ Ag. I-ot C11. F l i i (2.11)} !
-l ,
where:- 3 D, = the cumulative dose conunitment to the total body or an. organ, T, from the-liquid effluents for the. total' time " period I ot , in mrem. i E
. I 2-8 Rev. 10 i
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J FNP-0-M-011 1
-Liqui _d Effluents: j Ag: = site-related adult ingestion dose' comitment' factor' to -
the total-body or organ,;t,fforJeach identified . radionuclide in~ Table 2-4, in mreivhr per pCi/ml. At = length of the time period over which C J and F lare 3 ! averaged,-for.allliquidreleases,-:in.bours. 3 f C13 = the. average -concentration ofl radionuclide, i, in ; undilutedliquid~ effluent'duringtime.periodot[from} : Mrj liquid release, in pCi/ml. ' 1
^
F1 = the near field average dilution. factor for c-.6'during i any liquid effluent release.. F' is' defined as the-ratiooftheaverageundiluteddiquidwasteflowduringj : release to the product-ofithe-average. unit flow from' ' the site-discharge structure to unrestricted receiving: waters times 5.' . (5 is the site specific applicable: ; factor.for: the mixing effect'of'the discharge. 4 structure.) ' 1 1 u.p n 7 , ^{ F,
- 51 with the: limitation that- 4 1' ,
F,
- 5 $ 448,800 gpm. _1000
( cfs - reference 1 L The values of An shown in Table'2-4 are-calculated fromt U
-1 Ag =k,(U,:BFj'+U,CFi y ] DFg -(2.13);'
where: ' I k= unit conversion factor 1.14.x'105 (year /hr).(ml/1).(pci/uci); , 1 h adult fish. consumption, 21 kg/yr. (reference 4) U, = ' l , BF i = the bioaccumulation factor -(Table -.2-2) in; fish for' each! -t H measured radionuclide i, in pC1/kg per pCi/ liter (Table- !; A-1 of Reg. Guide 1.109, Ref.'4)' . t Uy = adult vegetable consumption, 64'kg/yr'(reference 4)" i' 2-9 Rev. 10
- (
i o . j
.i F
l 3 i
. -t . ._. _ . . - , _ . _
.- k-.- - ..
s FWP-0-M-011 4 J. . Liquid Effluents-Crg y ~, 4 concentration factor for radionuclide i in the vegetable,: pCi/kg/pCi/1 4 o for radionuclides other than tritium , P
- M.I r(1-e [,) f, ' B g (1-e'*,()'I 4 ,
---- + -
e ,,
- YJ\r .P A3 .
(2.14)(ref.i4)' j
' for tritium.
l
= Mr (2.15)(ref. 4) '
Drg _.=.,the ingestion, dose conversion factor-(Table 2-3) for-each > l organ, t, ' for each nuclide, i, for adults, in ' mrenVpci a
.(Table E-11 of Reg. guide 1.109, Ref. 4).
4 M= additionp'1 river dilution at the' point of irrigation usage . , (4 x 10' using actual: river flow data for 1989 as a.typicals: ' year) s J j} I= averageirrpgationrateduringthegrowingseason,.1/m*/hr- (1.261x 10' estimate based on pump capacity and garden size from reference 6 for 10% of the. time). -, 1 r= fraction of deposited activity retained on leafy. vegetables',7 1.0 for lodines;and 0.2 for_others (reference 4). a ' b Y, = agricultural proeductivity, 2.0 kg/m*-(reference 4). I f, - thefractionoftheyearthatthevegetablesareirrigatled -i (0.1, estimate based on reference 8).
~
Bg
=, crop to soil concentration factor, pCid g leaf per pCi/kg soll, Reg. Guide 1.109,' Table E-1 (reference'4). '
~
P. effective surface density _for. soil' 240 kg/m 3( refererce 4 ) . . l A 1
=
decay constant for radionuclide 1 (reference 10)., (= rate constant for removal of activity from a plant ' leaf-
-(half-life.- 14 days), 0.0021'hr' L(reference.-4).1 '
_ AE = (- + X[-(effective removal rate-for radionuclide'i from 3 4 crops,_ reference.4)'. t, = -period of leafy vegetable exposure during growing season, 60 days (1440 hours) (reference 4). ' t, = period of long tprm activity bu' ldup i in soil -(norainally 15. years) 1.31 x 10 hours (reference 4). i l 2-10 Rev. 10 s i, s <
- - - , . . . , . - ,, , 4 - . , - , . , , ,s.-
,L' ,
n;
. , , - i IWP-0-M-011- i Liquid Effluents-
- t,' = { time ~ delay between harvest'of vegetable and consumption by
~
' man, 24 hours (reference 4). '
- 2.5 COMPOSITE ANALYSES; ,
i For radionuclides:. not determined' in 'each- batch or- weekly 1 composite, the dose contribution. to the current calendar month or.- quarter cumulative. summation. may be approximated by assuming :an'
- average monthly or quarterly ' concentration based on the previous monthly or quarterly composite analyces. The nuclides determined-f rom composite analyses . are ' H-Jf,i Fe-55, ;Sr-89, Sr-90, and gross.
alpha.
~
'2.6' DOSE PROJECTIONS ~
- Doss projections:shall;be made at least! once:in every 31 days, for all . liquid: effluent doses, based -oni the expected. operating; '
conditions,s - Thes. ~ dose projections ;will- belcompared to the.- . projected dose limic mf 0.06 mrem for thettotal bodynand 0.2 mrem: "! for any organ.- These line s are for the month. O
~
Q
-t d
1
. o i
d i 1 l i a
^1 2-11 Rev. 10 A
_j i t
)'
= _ . _ _ _ _ _ _ = _ _ _ _ _ _ _ _ _ _ . . _ . _ . _ _ _, . _ . . , ,, , . _. i. .
- i
- 8 M ', ]
- l. - ,
l , d' , Liquid Effluents
.fNP-0-M-011 4
-j i
l
! Bioaccumulation Factors for Fresh Water fish Bioaccumulation Factor-for.
Element Fresh Water Fish _- H 9~00E-01 C 4.60E+037. NA 1.00E+02. 1
,P ~3.00E+03 (Reference 7),
CR- 2.00E+02i :)1 MN -4.00E+02 ! FE. - 1.00E+02- '
- Il CO! 1 5.00E+01-1
.NI 1.00E+02 CU ~ 5.00E+011 ZN 2.00E+03 BR . 4. 20E+02 c-RB 2.00E+03
'SIL . 3.00E+01 1 Y. -2.50E+011 .o u ZR s
'3.30E+00; HNB' 3.00E+04:
MO 'j' 1.00E+01:- TC. 1.50E+01, , RU -1.00E+01r i RH 1.00E+01~ TE- 4.00E+02-I .1 '. 50E+01' ' CS :2.00E+03 -! BA 4.00E+00 $ LA . CE 2.50E+01
-l'00E+00:
j PR :2;50E+01 .)o ND -- 2. 40E+01L W 4 { 1.20E+03' W NP 1.00E+01= SB 3.00E+02-(Reference.11) AG '2.30E+00 (
Reference:
9) Units are pCi/Kg per pCi/ liter , l
-i i
Table'2-2. Bioaccumulation. Factors (Ref. 4,fexcept as, indicated)
'h 2-12 :Rev.-10 3
.-~
;c' .
e. A
. y; I
FNP-0-M-011.
. Liquid Effluents ;
INGESTION DOSE CONVERSION FAC'IORS i Nuclide~ Bone Liver. T. Body ~ Thyroidi Kidney; Lung GILLLI- i 4 H-3: 0.00E+00 .1.05E-07: 1.05E 1.05E-07 1.05E-07 .1'.05E-07 1.05E-07 ' C 2.84E-06 -5.68E-07 5.68E-07 5.68E-07: 5.68E-07 5.68E 5.68E-071 1NA-24 1.70E-06 1.70E-06 1.70E-06D 1.70E-06 '1.70E-06:'1.70E-06' 1.70E-06 P-32 CR-51: 1.93E-04' l'.20E-05 7.46E-06 .0.00E+00 0.00E+00 0.00E+00: 2.17E-05
-0.00E+001 0.00E+00" 2.66E 1.59E-09 5.86E 3.53E-09 6.69E-07 j
J MN-54 tf 0.00E+00 4.57E-06 8.72E-07' O.00E+00: 1.36E-06. 0.00E+00l 1 40E-05 l MN 20.00E+00E1.15E-07 2.04E-08 0 .00E+00 '1.46E-07 0.00E+00',3.67E-06 FE-55 2.75E-06!-1.90E-06 4.43E-07 .0.00E+00 0.00E+00 1.06E-06 .1.09E t FE 4.34E-06" 1.02E-05. 3.91E-06 'O.00E+00 0.00E+00' 2.85E-06 ~3.40E-05 Co 0.00E+00 7. 45E--07 : 1.67E-06. 0.00E+00 0.00E+00L 0.00E+00 1.51E-05i ; co-60 0.00E+00 12.14E-06 '4.72E-06 .0.00E+00~ 0.00E+00: 0.00E+00- 4.02E-05 s NI-63' 1.30E-04.-9.01E-06 4.36E-06 J0.00E+00 -0.00E+00 0.00E+00' 1.88E - > NI-65 5.28E-07 6.86E-08? 3.13E-08' O.00E+00 0.00E+00- 0.00E+00 .1.74E-06K l. CU 0.00E+00a 8.33E-08: 3.91E-08 0.00E+00 2.10E-07 0.00E+00 '7.10E-06 a
!ZN 4.84E-06 1.54E-05 6.96E--06 0.00E+00 l'.03E-05. 0.00E+00 9.70E-06 ZN-69. 1.03E-08 1.97E-08 l'.37E-09 :0.00E+00 - 1.28E-08 0.00E+00' 2.96E-09' BR-83' k BR-84
-0.00E+00 0.00E+004'.02E-08 0.00E+00 0.00E+00 0.00E+00. 5.79E-08: J BR-85 0.00E+00 c 0.00E+00 - 5.21E-08: 0.00E+00. 0.00E+00 0.00E+00 4.09E-13' '
RB-86' 0.00E+00 0.00E+00.12.14E-09.- 0.00E+00.'O.00E+00 f0.00E+00'!0.00E+00 , O.00E+00 2;11E-05 9.83E-06 -0.00E+00: 0.00E+00: 0.00E+00- 4.16E-06 , RB-88 RB-89 0.00E+00 6.05E-08 3.21E-08 0.00E+00 0.00E+00 0.'00E+00f8.36E-19 SR-89' 0.00E+00 '4.01E-08i 2.82E-08 10.00E+00' O.00E+00~ 0.00E+00 2.33E-21' J
- SR '3.08E D.00E+00~ 8.84E-06' 0:00E+00 0.00E+00 0.00E+00 4.94E j SR-91 7.58E-03 0.00E+00 1.86E-03 J0.00E+00 .0.00E+00 0.00E+00 2.19E q 5.67E-06 0.00E+00 2.29E-07 0.00E+00 0.00E+00. 0.00E+00. 2.70E-05 d l SR-92 Y-90 2.15E-06 0.00E+00 9.30E-08 0:00E+00 0.00E+00'.0.00E+0014.26E-05 t 9.62E-09 0.00E+00 -2=.58E-10' O.00E+00 0.00E+00' O.00E+00';1.02E-04 Y-91M Y-91 9.09E-11 0.00E+00 : 3.52E-12 "0.00E4 00 0.00E+00: : 0.00E+00 2.67E-10 , l, Y-92.
1.41E-07 0.00E+00 3.77E-09. 0.00E+00 -0.00E+00 -0.00E+00 7.76E-05. 1 8.45E-10 0.00E+00 2.47E-11:~0.00E+00' O.00E+00 0. 00E+00 -- 1. 48E j h j SB-124 .2.81E-06 5.30E-08 1.11E-06; 6.79E-09 0.00E+00" 2.18E-06l 7.95E-05 'I SB-125 2.23E-06 2.40E-08 4.48E-07 1.98E-09 0;00E+00:'2.33E-04 1.97E t Units are arenVpci o d Table 2-3. Ingestion Dose Conversion Factors (Ref. 4, except SB'(Ref. 9)) > l l- 2-13 Rev.,10 1
'i l' \
b
FNP-0-M-011
' Liquid Effluints 1
l Nuclide Bone ' Liver T. Body Tnyroid- Kidney Lung 'GI-LLI
'l Y-931 2.68E-09' 0.00E+00 7.40E-11 0.00E+005.0.00E+00 0.00E+00x 8.50E-05
/ZR-95' 3.04E-08 9.75E-09 6.60E-09:.0.00E+00 1:53E-08 0.00E+00 3.09E-05' 1 ZR-97 1.68E-09 -3.39E-10' 1.55E-10E 0.00E+00. 5.12E-10 0.00E+00- 1.05E-04~ '
NB-95' 6.22E-09' 3.46E-09' 1.86E-09 0.00E+00l-3.42E-09 0.00E+00 2.10E-05
.j l-i MO-99 0.00E+00 4.31E-06 !8.20E-07i 0.00E+00 9.76E-06 0.00E+00L 9.99E-06 i
~
!~ K-99M- 2.47E-10 6.98E-10 ,8.89E-09: 0.00E+00 1.06E-08. 3.42E-10' 4.13E ' K-101 2.54E-10 3.66E-10: 3.59E-09' O.00E+00: 6. 59E-09 V1.87E-10 : 1.10E-21 RU-103 1.85E-07 0.00E+00 L 7.97E-08 .t.00E+00 : 7.06E-07; 0.00E+00 ' 2.16E-05 RU-105. 1.54E-08 0.00E+00 6.08E-09i 0.00E+00 1.99E-07 :0.00E+00' 9.42E-06 RU-106 ' . 2.75E-06 0.00E+00> 3.48E-07 0.00E+00 '5.31E 0.00E+00r 1.78E-04 AG-110M ' 1.60E-07 1.~48E 4 07 8.79E-08: - 0.00E+00 a 2.91E- 07 0.00E400H6;04E ,
,TE-125M12.68E-06: 9.71E-07 3.59E-07 '8.06E-07 1.09E-05. 0.00E+00; 1.07E-05.
)
s TE-127M 6.77E-06 ~2.42E-06-'i8.25E107. 1.'73E-06? 2.75E-05' 0.00E+00 ?2.27E TE-127 1.10E-07 3.95E-08 -2.38E-08Hc8.15E-08 4.48E-07 .0.00E+00. 8.68E ; TE-129 C 1.15E-05 4.29E-06' 1.62E-06 3.S5E-06 -4.80E-05 'O.00E+00. 5.79E i TE-129' 3.14E-08 '1.18E 7.65E-09. 2.41E-08::1'.32E-07 0.00E+00- 2.37E-081 o TE-131M 1.73E-06' 8.46E-07' 7.05E-07 1.34E-06o 8'.57E-06 :0.00E+00"8.40E-05
'I TE-131 1.97E-08 8.23E-09 6.22E-09 L1.62E-08: 8.63E-08 0-'00E+00. 2.79E-09 .
TE-132 2.52E-06 .1.63E-061 1.53E-06 11.80E-061 l'. 57E-05 : 0.00E+00 7.71E-05: I I-130 '7.56E-07-' 2.23E-06, 8.80E-07 1.89E-04 3.48E 0.00E+00: 1.92E ' l I-131 4.16E-06 5.95E-06 3.41E-06 1.95E-03 1.02E-05 0.00E+00,?1.57E-06 j I-132 2.03E-07 5.43E-07 :1=90E-07: 1.90E-0 E 8.65E-07'-0.00E+00 1.02E-07 I-133 1.42E-06 2.47E-06~ 7.53E-07 3.63E-04> 4(31E-06 -0.00E+00<~2;22E-06i I-134 1.06E-07 2.88E-07 :1.03E-07 t4.99E-06 4.58E-07 0.00E+00c 2.51E-10 I-135 4.43E 1.16E-06' 4.28E 7.65E 1.86E-06= 0.00E+00 1;31E-06x CS-134 6.22E-05t-1.48E-04' 1~.21E-04 0.00E+00LL4'.79E-05 1.59E 2.59E CS-136 6.d1E-06. 2.57E-05 .1.85E-05 0;00E+00 ;"1.43E-05 E1.96E-06 . 2.92E-06 CS-137 7.97E-05 ,1.09E-04. 7.14E-05 0.00E+00 J3.70E-05 1.23E-05 2.11E-06 CS-138 5.52E-08 1.09E-07 5.40E-08:'0.00E+00 '8.01E-08 7.91.u-09= 4.65E-13 : m-139 9.70E-08 6.91E-11 2.84E-09 LO.00E+00: 6.46E-11 -3.92E-11 '1.72E-07 BA-140 2.03E-05 2.55E-08 1.33E-06. 0.00E+00' 8.67E-09 :1.46E-08 4.18E 1 BA-141 4.71E-08 3.56E l'.59E-09 0.00E+00 -'3.31E- 11 2.02E-11 E 2.22E-17 1 l BA-142 2.13E-08 2.195-11 1~.34E-09 m0.00E+00 1.85E-111 1.24E-111c3.00E-26 l' LA-140 H 2.50E-09 1.26E-09 l3.33E-10 10.00E+00'~0.00E+001 0;00E+00 .9.25E-05 'l LA-142 1.28E-10 5.82E-11 1.45E-11 0.00E+00~.-0.00E+00' 0.00E+00 4.25E-07 -' CE-141 9.36E-09 6.33E 7.18E -10 l0.00E+00 ; 2.94E-09 3 0.00E+00. 2' 42E-05 CE-143 1.65E-09 1.22E-06;-1.35E-10 -0.00E+00 :5.37E-10 0.00E+00' 4.56E-05 *)
, CE-144 4.88E-07 2.04E-07 2.62E-08 0.00E+001 1.21E-07 0;00E+001.65E-04" n PR-143 9.20E-09' 3.69E-09 ;4.56E-10 0.00E+00'~2.13E-09 0: 00E+00;'4.03E-05= 'l PR-144 '3.01E-11? 1.25E .1.53E-12 l0.00E+001(7.05E-12 .0.00E+00- 4.33E-18 ND -147 6.29E-09 7.27E-09' 4.35E-10 0.00E+00 4.25E-091 0.00E+00: 3.49E-05 W-187 .1'.03E-07 8.61E-08 3.01E-08: 0.00E+00! 0.00E+00 0.00E+00~ 2.82E-05 NP-239 1.19E-09 1.17E-10 6.45E-115?0.00E+00' 3'65E-10.'0.00E+00. 2.40E .
Uni'c are arenVpCi Table 2-3.- ' Ingestion Dose Conversion. Factors'(continued) l 2-14 Rev. 10-
'l
_ - . _ ~ ~ , . . _ ,
E, ' mP-0-M-011= *
% . Liquid Effluents)
I' 4 q
- LIQUID ErrLUENT DOSE COMMITMENT: FAC'1DRS Nuclide > Bone -Liver ~ 'T. Body Thyroid Kidney i Lung GI-LLI-H-3 Na-24~ 0.00E+00 2.57E-0112.57E 2.57E- 01 2.57E-01' ' 2.57E-01 2.57E-011
'4.07E+02 4.07E+02 .4.07E+02:;4.07E+02 4'07E+02 4.07E+02 4.07E+02c CR-51' MN-54 O 00E+00' 0.00r+00- 1.28E+00 17.63E-011 2.81E-01. 1.69E+00M 3.21E+02 0.00E+00 4.38E+03.'8.36E+02 0.00E+00 1.30E+03 0.00E+00, 1.34E+04- '
. MN i TE-55 -0.00E+0D <1'.10E+02: 1.95E+01' 0.00E+00 ' .1.40E+02 l0.0M+00 '3.51E+03 : 1 6.63E+02 4.58E+02 I'.07E+02_ 0.00E+00- 0.00E+00 2.W Z+02' 2.63E+02. - FE-59 1.04E+031-2.46E+03 ;9.41E+02 0.00E+00. 0.00E+00-16.86E+02 8.18E+03- '
.Co-58 4 L0.00E+00: 9.03E+01, 2.02E+02 0.00E+00 0.00E+00' 0.00E+00' 1.83E+03 1.
Co-60 : 1
-0.00E+00- 2.60E+02 5.73E+021 0.00E+00. 0.00E+00 0.00E+00 4.88E+03 KI-63 NI-65. 3.14E+04 2.17E+03' 1.05E+031 0.'00E+00 .0.00E+00 .0.00E+00?14.53E+02-CU-64' -1.26E+02:'1.64E+01' 7.49E+00L 0.00E+00 0.00E+00f0.00E+00:'4.17E+02'. l ZN-65' 0.00E+00' 9.97E+00 4.68E+00 0.00E+00 c2.51E+01' 0.'00E+00 '8'.50E+02=
BR 2'32E+04 7.38E+04 J3.33E+04 0.00E+00 4.93E+04' 0.00E+00 4.65E+04' -
~
0.00E+00 >0.00E+001 4.04E+01 L0.00E+00 0.00E+00 z0.00E+00' 5;82E+015 RB-86 '
-SR ' O.00E+00 : 1.01E+05 - 4.71E+04 - 0.00E+00 O.00E+00 10.00E+00' 1.99E+04: ' ,
2.25E+04 0.00E+00 6.47E+02 0.00E+00. 0;00E+00 -0.00E+00- 3.62E+03 SR-90 - 5.5BE+05 0.00E+00' 1.37E+05- 0.00E+00; 0.00E+00> 0.00E+00u 1.61E+04>
'SR-91~ 4 07E+02 }
SR-92 0.00E+00 '1.64E+01 0.00E+00 D0.00E+00' 0.00E+00: ~1.94E+03 '* 1.54E+02 0.00E+00l _6.68E+00 0.00E+00- 0.00E+00--0.00E+00 3.06E+03
.Y-90 1
'Y-91 5.78E-01 0.00E+00 1.55E-02 0.00E+00 10.00E+00 ~0.00E+00 6.13E+03' Y-92 8.64E+00. 0.00E+00' 2.31E-011 0.00E+00' O.00E+00 0.00E+00t 4.75E+03' Y-93 5.06E-02 -0.00E+00 l'.48E-03 -0.00E+00' 0.00E+00 0.00E+00. 8.86E+02 ZR-95 1.60E-01 0.00E+00 ,4.43E-03 0.00E+00'~0.0CE+00 0.00E+00--5.09E+03 2.84E-01 9.09E-02 -6.16E-02! 0.00E+00' 1.43E-01E 0.00E+00- 2.88E+02 m
ZR-97 ~ NB-95 1.33E-022.~49E+02 4.47E+02 2.69E-03 1.23E 0.00E+00 ' 4'.06E--03' O.00E+00 0 8.33E+02-1 MD-99 l'.34E+02- 0.00E+00 2.46E+02'.0;00E+00 l'.51E+06 ' 2C-99M :0.00E+00 1.04E+02 1.98E+01 -0.00E+00' 2.36E+02. 0:GOE+00. 2.41E+02 RU-103 8.87E-03 2.51E-02 3.19E-01 :0.00E+00 3.81E-01-- 1.23E-02 1;48E+01 4.66E+00 0.00E+00 2.01E+00 0.00E+001.1.78 h 01 0'.00E+00 5.45E+02 RU-105 ' 3.69E-01 0.00E+00 1.46E 0.00E400l 4.76 m00L-'.00E+00 0 2 26E+')2 RU-106 . 7.05E+01 0.00E+00 8.92E+00 0.00E+00 J1.36E+02, 0.00E+00 4.56E+03- - '* AG-110M -1.15E+00 1.06E+00 6.31E-01 -0.00E+00 -2'09E+00 0.00E+00 '4.34E+024 TE-125M .2.57E+03 19,31E+02 3.44E+02: 7.73E+02 1.05E+04' O.00E+00~ 1=.03E+04-1 TE-127M- 6.49E+03' I.32E+03- 7.91E+02 1.66E+03 2.64E+04 10.00E+00 .2;18E+04-Ur.its are mrenyhr per C1/ml-
. o Table 2-4. Liquid Dose Comitment ractors Ai
,s 2-15 Rev. 10
-l J
5 L L
,=
q lHP-0-M-011 i Liquid Effluents-j Nuclide Bone Liver +T. Body. ' Thyroid. Kidney -Lung' GI-LLI TE-127 1.05E+02 3.78E+01 2.28E+01 -7.80E+01. 4.29E+02: 0.00E+00 8.31E+03' TE-129M: 1.10E+04.' 4411E+03 '1'.75E+03 3.79E+03 4.60E+04~ 0.00E+00 5.55E+04 1 TE-131M -1.66E+03 8.10E+02 6.75E+02 1.28E+03 .8.21E+03 .0.02+00 8.04E+04 l TE-132- 2.41E+03 1.56E+03: 1.47E+03 1.72E+03 :1.50E+04 0.00E+00 7.39E+04. -{
-I-130 2.72E+01-- 8.03E+01 .3.17E+01L 6.80E+03. 1.25E+02- 0.00E+00. 6.91E+01 t I-131 1.62E+02 2.31E+02 1.33E+02 7.58E+04 3.97E+02 0.00E+001 6.10E+01~
I-132 7.29E+001.95E+013 6.82E+00 -6.82E+02. 3.11E+01 0.00E+00 3.66E+00' I-133- 5.13E+01:'8.93E+01~ 2.72E+01: 1.31E+04 1.56E+02. 0.00E+00 8.02E+01 1 I-135 1. 59E+01- 4.17E+011~1.54E+01 2.75E+03 6 '. 68E+01 ' O.00E+004-71E+01 . 1 CS-134 2.98E+05.:- 7.09E+05" 5.80E+05 0.00E+00' 2.29E+05 7.62E+04 '1.24E+04 CS-136. 3.12E+04 1.23E+05 >8.86E+04. 0.00E+00 6.85E+04, 9.39E+03.-1.40E+04 CS-137 3.82E+05' : 5.22E+05 3.42E+05 0.00E+00 1.77E+05 5.89E+04 1 1.01E+04 : BA-140 2.11E+02 2.65E-011: 1.38E+01'0.00E+00 9.00E-02 .1.51E-01 4.34E+02 LA-140 1.50E-01:'7.56E-02 2.00E-02 '0.00E+00 0.00E+00" 0.00E+00!i5.55E+03- 1 CE-141 3.37E-02 '2.28E-02 -2.58E-03 0.00E+00'.1.06E-02 '0.00E+00 J8.71E+01 ' CE-143' '4.11E-03' 3 04E+00 -3','36E-04 0.00E+001-1.34E-03 0.00E+00 1.14E+02' CE-144 1.98E+00 8.28E-01 1.06E-01 ~ : 0.00E+00 4.91E-01" 0.00E+00 6.70E+02 ,
.i PR-143. 5.58E-01 2.24E-01= ' 2.77E-02. :.0.00E+00' l'.29E-01 -0.00E+00,.2.45E+03~ t ND-147 3.81E-01 4.40E-01 2.64E-02. 0.00E+00' 2;57E-01' O.00E+00n2.11E+03 ,
W-187 2.96E+02 2.47E+02 8.65E+01 0.00E+00 '0.00E+00.'0.00E+00 8.10E+04 6
,NP-239' Sb-124 2.87E-02 2.82E-03 -1.56E-03 0.00E+00' 8.81E-03 0.00E+00J 5.795402
'1.75E+03 - :3.31E+01 ' 6.92E+02 4.24E+00: 0.00E+00 :1.36E+03 ~4.96E+04 Sb-125 1.39E+03 .1.50E+01 2'.80E+02;'1.24E+00 .0.00E+001.45E+05. 1.23E+04 '!
Units are mrenVhr per Ci/ml
- l. , ,
l p r 1 6 .~ i y 1; L Table 2-4. Liquid Dose Commitment Factors-A1 (continued) ; 2-16 Rev. 10 l [ l l
. __ ___._R-. --__=_:----.
i
' b
_ 4) 4 . .;- : . > s .- j 3 , FNP-0-M-Oll o, l t m .! C s ;. CHAPTER 3 e
,' GASEOUS EFFLUENTS . L u
3.1. GASEOUS RELEASE CONFIGURATION . d Gaseous releases-Leonsist . of! releases . through i three~ different f i release points: I o- Plant vent stack' ' s o Turbine building ~ vent '(condenser ' steam 1 jet air. ejector): - o-1ILRT (integrated leak rate. test) vent
'Ihe ' containment ventilation, the auxiliary building ventilation,'-
'and the waste gas decay tanks all exhaust throughi the plant; vent:
1 stack. When' a waste gas decay tank is released,' this isj treated as, a contribution to the- continuous release t already occurring
- through the - plant vent stack. 1 All: other releases through the plant vent stack are continuous. The turbine buildingyvent isLai-continuous release also. The ILRT is .a batch' release,(performed
' infrequently.. 1 The plant vent- stack is a mixed, mode : release, L.according :to : the: d definition in Reg. Guide 1.111'. The1 release ~ vent is ' at' a -
~
comparable, height to adjacent structures '(the , - stack and: . 1 containment building are.both approximately 40 meters'high). All other releases: are ground level ~ releases.:. Y cschematic. diagram of the routine release points and release:isources and - monitors is shown in Figure 3-1. i j
- Typical flow rates (where applicable).for'each release ~ source and.
-T release point are given in Table 3-1.
J 3 3 'Rev. 10
't l s
' 4'
, , f( 1-9
se . . ; FNP-0-M-Oll-
'm.,
Gaseous. Effluents 'J Table.3-1. Gaseous' Releases, Flow Rates, and Monitors
.J
. Release point Release g ' Vent flow rate Monitor M Plant vent stack- continuous 80,000-150,000 cfm 1/2RE-14 f 1/2RE-22 Turbine building vent . continuous 1,060 cfm 1/2RE-15 ILRT. >
-batch -- -
4 M Release' sources: Waste gas decay tank ' batch' - 1/2RE-14 > Containment purge continuous
~1/2RE-24: ,
?
q Release- processing: of the waste 1 gas -decay tank ~ (WGDT) and containment purge releases are made through the plant; vent stack.
.['
-l The? WGar Curie content is . tracked separately .for . Tech. Spec. O compliance. Activities and dose ' from the plant , vent stack are.-
tra::ked - to account for .all activity release;from containment and ~ the auxiliary building. Containment - purge = activities ~ - and calculated doses are -not added 'into; the total activity. and" dose.- , released since they are included in the meas"rements of plant vent-
- 'I stack activity. . l-WGDT activity and dose are separately calculated .and tracked as :(
batch releases. To eliminate--double counting,1 for each " plant stack- release,'if there was a NGar batch release,:the individual c WGDr nuclide activity and dose are subtracted from the plant; vent [ stack release for the time'of the WCDT release. 'If any nuclide ' activity'is negative, Jt is set'to zero.- i h
'!l 1
l l 3-2 Rev. 10 ., l l
< 1 1 :.
, .7 _ . . - . . - . . _
gy; L.. .
- J ,
si . 4 j-; Gaseous'Effluente FNP-0-M-011- .;
. f; - . .
Waste Gas Decay: Tanks c E
. ll' ]l k -
- r. 3r ir ir- 1 r-3r.
L Ja Jk Jh dk 3r 3r w ___ as n- JL i 7 '8 1 , 2' 3 '.
~14 5 6- '
i r -3r; i r> -i r 1 r s -i r 1r 17 Ji JL. d b .d k .dA 4 i- -- Jh ~< - dA ,
'i 3r 8 r.. 't.
Jg b" :1 v -a dk' t
] , ;, Waste Gas-RE2 13 MON TOR . Compressor ;
.g i 3
f - ?-- PLANT VENT STACK
.U- (E-1 5
~'#
.lLRT ilk'T"- RE-22 MONITORS
- VENT-o _
CONTAINMENT AUX- -' CO _ PURGL BLDd. MEN -
.. EXHAUST PLENUM RE-24 "*
MONITOR
- AUXILIARYs ,
BUILDING - ' RE-15 MONITOR TURBINE ' TURBINE- , BUILDING'. O BUILDING'- ' VENT i i 1 \ .1 Figure 3-1. Routine Gaseous Release Sources and Release Points 3-3 Rev. 10 l l l 6 9 * .* + ,e'=. ___________--'_._.___m___-_m_E.___'___mm____-
q . m r- 4,
* - FNP-0-M-Oll' Gaseous Effluents'
- 3.2- CALCULATIONS O!" X/Q AND D/Q VALUES L'Ihe calculations of .X/Q and D/Q valves are based on the constant-s
= wind speed model -described in Reg. , Guide- 1.111, Rev. : 0 - (March;
-1976), and Rev.1. (July,1977), sect!_ons C.l.c, C.2.a, C.2.b, and :
C.2.c. As noted in section 3.1,- the p int vent stackL is a mixed . j mode releasei and the turbine building vent and ILRTf are ground = .l level' releases. A mixed mode . release is handled by using portions ' of ground and elevated release values -in combination with-. a . factor,- E, representing the degree of n entrainment of the release in the. building wake. . If it should happen that the ground' and= elevated values are:in different sectors,.the doses'and activities' will be' attributed-' tot the proper sector for : each - of .the ground and ; elevated releases. 1 Mixed Mode.X/Q and D/Q i
'Ihe mixed mode X/Q value is obtained- from 'the equation X/Q = ( (1-E)(X/Q),3, y . + E(X/Q),,,) QM 'i where ,
s, E = fraction of effluent entrained in the building wake. ! (X/Q),3,y = X/Q value for' elevated release-y (X/Q),,, = W W gmd hel release ! similarly for D/0 vr a the mixed mode' D/0 valueE is obtained-
, I fr;m the equation j
D/Q = ((1-E)(D/Q),3,y + E(D/Q),nd } (3.2) " where H.' E.= fraction of effluent entrained in the building wake ! (D/Q),3,y = D/Q value for elevated release !
.c [
(D/Q),,, = D/Q for ground level release 1 1 l 1 i
-- i j
s Q Yl l 3-4 Rev. 10 1 r ; im
\
FNP-0-M-011 i Gaseous Effluents j E is determined from the followint, equations, depending upon the rangeofthevalueof(W/u): (3.3) ! E=1 if (W/u)$'l i or h, $ h, E=1.58-1.58(W/u) if 1<(W/u)51.5 l E=0.3-0.06(W/u) if 1.5<(Wfu)$5.0 ; E=0 if (W/u)>5.0 s where W, = effluent velocity from the' stack-L = average wind speed Ground Level XM - Ground level releases - (turbine ' building - vent and ILRT) use the ; following calculations for X/Q, which are taken from Reg. Guide 1.111. i (XM)3 , = 2.032 k,/.(b, r, I,) (3.4) ; where the subscripts j W are for hour j, sector 0, and vent v. I, = ( o#, + 0.5h* /n)*' (3.5) where I, is subject to the condition. I I, 5 (3)* a, (3.6) The values of a, are shown in Figure 3-2' for - all stability cla6ses. r The parameters used are i 3-5 Rev.-10 l L IL ,, m I
.. . l
' FNP-0-M-011 1
. Gaseous Effluents l I
2.032 = (2/n)U# divided by width of 22.5 degree sector in radians e, = the verticalistandard deviation of the plume for the ' applicable atmospheric stability class (Pasquill category) ' determined at least hourly, for ti?e distance r, during the time period 6tj (rigure 3-2). t r, = the distance from the midpoint between the vent stacks to- i the-receptor for each sector 6, in meters, provided in : Table 3-2. ; k, = the recirculation factor accounting for spatial and ., temporal variations in air flow. For noncontinuous releases, its value is unity. For continuous releases,- 1 see rigure 3-3 for correction factor. Q, = the aversge wind speed determined at least hourly, during time period at in sector 0, at a height of 10 meters for ! groundlevelrAleases,-innVsec. , h, = the height of the tallest adjacent structure, which is the I containment building (=40 m). +
?
\
i 1 i ? l 4 l L;
;i r
i 1 1 3-6 Gen.'Rev. 7 I l
?
l: I i i t
, - - , , , y ,.- - ,.v. -
c ..
' FNP-0-M-011 ;
Gaseous Effluents TARLEY NUCLEAR PINTI VALUES OF SEC20R DISTANCES ; l SITE BOUNt%RY NWtEST RECEP70R ! SEC7OR DISTANCE -DISTANCE' (meters) (miles)- (meters). (miles) , N 1290 0.8- 4183 2.6. 1 WE 1450 0.9 4023 2.5 NE 1450 0.9 3862 2.4 ! mE 1450 0.9 3862 2.4 . E 1290 0.8 4505 2.8 l ESE 1290 0.8 4505 2.8 3 SE 1450 0.9- 5471 3.4 . SSE 1610 1.0 8045 5.0- t S 1610 .0- 6919 4.3 p SSW 161^ 0 .4666 2.9 SW 1450 0.9 i 1931 1.2 1 WSW- 1450 0.9 3862 -2.4 W 1290 0.8 2092- 1.3 I WNW 1290 0.8 3379 2.1 m 1450 0.9 2414 .1.5 3 ftM 1450 -0.9 3218 2.0 ; i This table may be un'tited based on annual land census results as required in STS Section 3.12.2. , i b a a 3-7 Gen. Rev. 7 l F [
?
- . - -- , , .- - . ~ - . , !
o ,. 1. j l . ; I i i' l
. Gaseous Effluents FNP-0-M-011 l 6
I ~ l
\
1000 ; i .I ;,
; - :?
, l } =
, i
- 1. 1 i s. ;
l ~/ s
- f. - ,
i r r J ,# ,s "* l ,
.l
) f f ' ;
/
r }
/ / / *'*
- l c ,0, A
l ' s , , - p /. y p *
> ," f f i (- _r_ / 1 , s .
l' $ ,, ; F . F - j / " s j', r I- J , Y # . / ) a n * " & r
" "1,
~
g / f / jgrf , ( /
/{/ }V / , ,,, s
~
y / /// / 0 10: - f f f , 7 1 > .
/ / f 2 r .
/I / / '
?
/ /
/
'/ ~f I
l f /f .\
/
1 0.1 i j .i 1.0 10 100 - PLUME TRAVEL DISTANCE (KILOMETERS) , Figure 1. Vertical Sta-derd Deviation of Maurielin a Mums (Letters denote Pasquilt Stability Class) Figure 3-2.. Vertical Standard Deviation for.the' Plume (Ref. 3)' - 3-8 Gen. Rev. 7 ;
9 Guseous' Effluents FNP-0-M-011 a s ==- t i --
, _e. ~ . .- -
4 - -
._ . . . } .__ . . -
N . .. . . -
\,
5
\s u i.e ._ _ . ..
s%
= i -
=
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~
-I
- . . . ~ - - . .. .
I a.: < u.1 i
).o 10 -
DISTAtJCE (g:Longygng 100 Figure _3-3-. Recirculation Factor kg (Ref. 2) I
- 3-9 Gen. Rev. 7 g
. l ' FNP-0-M-011 Gaseous Effluents j Elevated X/O The elevated XA) value is given by:
(XA)),3,, = (2.032 k,/(0,3,, r,.e,)) ,-((h,/o,)'/2]- (3.7) where h - effective plume height
= h, + h,, = hr -c (3.8) ,
c = correction for low relative' exit velocity of the plume when W, / L,3,, is less than 1.5. 3
= 3(1.5 - W,fu,3,y)d- (3.9).
d - inside diameter of stack ' W, = exit velocity of the plume 0,3,, = average elevated wind speed h,, = plume rise h, = height of release point h, = terrain height above stack base ' h,, = 1.44 d (W , fu,3,,) '(rf/d)* ~(3.10) : subject to ., h,, < 3(W, fu,3,y)d g3.11)- '
.c
. i l
3-10 Gen. Rev. 7-l 4.. g <
-[
FNP-0-M-011 Gaseous Effleunts hy < 1.5 (r,/u,3,y)*" s~2" ifs >0 (3.12) where
- F, = (p,/p) w', (d/2)# (3.13) s - (9.8/T) (aT/az + 9.8 x 10'#) (3.14) where a, is the ambient air density p is the effluent air density S is the stability parameter with T.in' degrees K z in meters since the temperature of the air released is primarily that of' the -
auxiliary building, the value of (p,/p) w. x set to unity.- Ground and Elevated D/Q ror grcund level releaseh, the hourly (D/Q)3,, is given by (D/Q)3,, = k, f, 8,,,3 / (0,3927 r,) (3.15) whore j,, = subscripts ~for hour j, sector e, and vent'v. f, = 1 if the wind direction is into sector e and.is equalito zero otherwise. 0.3927 r, = width (arc length) of 22.5 degree sector at distance r, in meters. ground. level relative deposition rate (linear) at 8,y,3 = distance r, in sector e for stability class of interest and for ground level 3-11 Gen. Rev. 7 I I _
Gaseous Effluents release in meter-2 .- (rigure 3-4) ,
'or elevated releases, (D/Q),,, is given by i (D/Q)3,, = k. f, 6,,,, / (0.3927 r ) (3.16) !
where i 6,,,3 = elevated relative deposition rate-(linear) at distance i r, in sector 6 for stabilit l release height h, in meter'y class
. of interest (rigures 3-5, 3-6,and and :
3-7.), and all other terms were defined earlier. I t i
?
i e i l 1 s
. I 1
3-12 Gen. Rev. 7 :i i
.- . j i
6-
, Geseous Effluents FNP-0-M-011
\
I 1 i 194 -
'l i i
,, ,i,, , , , , ,,,,, , , i , , . . . . ,
l ut a i i i s oit i i a siiin i l 11 llll l 11llllll l l l-llllii l 1o 4 _
, x e ,
.....,x 3 , , , ,..... , , , . . . . . . .
i er l l l l 1 Itil Xl t i itill 1 iii,f88 1 i l l 1I ll 101 I N Ililil I l 1 Ililli g 1g i Ns i i , l 1
\ l g , , . . . . . . .
. .. X
, .;g , x,... ;
g i i i e iIllt i 1 1 1 11:11 l- I \1 # : ' r I I l l ll111. I I l illll I l IX!!i
.. I i I I
10 4 x
, s !
6 ,#,,,i e # , , sis,e , , ii . 1 I l l il til i l i i lIlit i l I l . Ii t; I I I l iiIlli l- l-l-Ililli l I I l!li!i 1 tg _ .. lll. - p 0.1 1.0 10.0 '100.3 230.0 = l ( PLUME TR AVEL DISTANCE (KILOMETER $1 menive o mi a to, c, uae L. i R== <An Arm...ner sus.licy can.o l i ! Figure 3-4. Ground Level Relative Deposition (Ref. 3).
- i 3-13 Gen. Rev.'7 l
l l~
+ - - .. - , , . , - -. . ,, . , . , , . , . . - . .-- - - . - . . - , = - -
. . __ _ _ _ _ _ _ .1 i
t Gaseous Effluents FNP-0-M-011 1 i 1 I 1 1r* _ i j i , ,. . . . . . . . . . . . . ! l l l 111ll I I i l lill l l I l l lIlI ' I I lilli l I Ililll 1 1 I I 111Il i ; v=:TAst L I l illi 3 "
,e m . s.eA.s....c.i ,
I
'n - .
4 g.- l
,,em
- h. .
g i /4 I lill W I l l NEUTRAL i i l'l llff; ; i I l/lllllll r W I-I lilli. l- 1Illill!- i i l E
, 3g /s:iiinn UTRAUD)
- i i i i iii- l l
372st si - ,, l} A I \ g , . . .,f s x
/i e i 3,. . ..
m . s, ) i; e i ,e,ep. Angi.
,E.
/i i i i i illi i i t. : ; /tii i N i iA
=
/ i l I i!!Ill l IIIiAlil. I l NJ ilhN i
,g
- iin 87 5 8(84,30 L .: xy i
li. \i '
' ~ ..
.w x
,r -
. , ,,,o,, , , , , , , , , , -
4 I I iitill i I A i!Itil -l I i i lit 18 i l I llllll, l:l/llllll! I l- I I lllii F 1 i . . is 1 ,-j. .) ! i - 0.1 1,0 10.0
' 100.0.- 2:3.0 ,i PLUME TRAVEL DISTANCE IK!LOMETIRS)
R.ia . o . n .oo,,, R.,,a it.,i .. . .. .n Stati,lity Class) .
'I 1
l l
.l Figure-3-5. Elevated Relative Deposition'--30Jm'(Ref. 3) l 3-14 Gen..Rev.>'
.l
, , + , , - , -. ,
+ e... - - .- - , - , , _ . - , , . , . - -
Gaseous: Effluents FNP-0-M-011 4 lb
. . , 1 .... e i . ..... i ...
e t w m iUNITatL E ta B C)
- iiee . . eie*e. ,
I '[l l l I IN l -l l l l1ill l-1 i l i iiti !
/ lI ll1ll- \ l l-l lllll- l l l llllll l Jr l !Ij I -
gyl / /fNtyTRALIDili i
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f e . r 'h s r i
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a II e i iiii+ . f ; i? . . . . . { 'l i l-i i Illi i lI ! I'lil I
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i i i / ili: 3 / l i IIIlll l- i ll_llill. l -- I l '/lllli I , i 1P7 f llll! STASLI'I*311. i
# . . ...i. . .
f i 6 i t i i sie e i a a4 eis. .- .g. , , - """ l I I I I Illli l i ilIlli i i/l l lla.. 9 II l I llllll L Illllill l 8/ l'l~lilh __. i _ itP4 l *
,,Il l] i
.6 81 1.0 io.o-soc.o No'o PLUME TRAVEL DISTANCE (KILCMfi s7. '
. Metative Deposition for Soms teleases (Letters cenote Pasovill sta i.tv c:.us i
Figure 3-6. Elevated Relative Deposition - 60 m (Ref. 3 ): 3-15 Gen. Rev. 7 ,
. . .t
,.. GOSOcus Effluent 8 FNP-0-M-011 i
l I Y .
. . i i..... . .
.. 1
)
4 6 9e: , t t #il#,e i e 6 i ..e. ll j l I 8 UNSTASLE lA.S.Cli l l 1
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i t g i i 1 i w E .[.... .,. [ NEUTRAL (0)..... N s . .] g < , e ....,f . e , _ , , 1 s.
..x . w i...
3 J l I lilll/ -1 1 I II ll l hQ l I N _[ /i l I lill/ I l ll L I l~ IKilllN I l l E-N ! l10-8 ll I l l i 1 i . > ..i. . . , . . . , , . . , f .Aiii i . i
. : i e s i si .6 eieis
[ / ' i l/l Illi l i i i Illi i 1 1 I ilill i ! (
.E. l ll/lllll.
l l' l l l llll- I l l lllll! .l . E STA8LI (E.F.Ci l l. g
\ l l NO CEPLETICN l gr7 ee l.
s i il I e 1 1 c e 1 . .. ,
. . . .6.. .
i , e/ i iee.ee e e ,ei ist i
, gi_ . i . l I l I lilli l l i lil 'il i _ l i18111 l IIlilll j
/ l I 'l l II'll ! i I I Illlll l 10** / I 0.1 1.0 10.0 '100.0 - 200.0
]
PLUME TRA'<fL DISTANCE (KILCMETERS) ReletwoCleas) Staiselity Demotetsen for 100m Releases (Letters senote Pasevill l R 1 rigure 3-7. Elevated Relative Deposition - 100 m (Ref. 3) . ! 3-16' Gen. Rev.'7 I I
I FNP-0-M-011 ( Gaseous Effluents 3.3 SETPOI!CS FOR CASEOUS M0hl'IORS 3.3.1 Alarm secpoints .*ar the gaseous ronitors ' R-14 R-15, ; and R-22 will be calculated based on the more ' restrictive of the dose rate -limits for noble gases-for whole body and skin. - These limits are expressed as 500 mrer/yr ry l [Kr iO,< (X/Q), x r. (3.17) ; 1 where 4 i ='subscrf,,t numbering noble gases in ! consir'eration, and the sum is over all noble gase. . Ki = the total body dose factor due to' gansna . emissionsfor.idenpifiednoblegasasotopei
.i (mrenVyr per uC1/m ) from Table S-3.- 1 Q , = release rate of isotope i-from release point 1
v (uCi/sec) l 500 = the site dose rate limit in mrenvyear-v = subscript indicating release point in consideration (turbine building vent or. plant vent stack) l r, = release fraction allotted to release. point in consideration. The sum of the fractions for the turbine building vent, plant-vent stack, and ILRT vent will not exceed 1 for each unit. (M), = highest value of annual average atmospheric dispersion fac or at site boundary for 611 sectors (se 1. (T/Q), = 1.08x10 sec/m for the plant vent stack 8 ( M ), = 4.87x10" *ec/m' for the turbine building i vent I r = unit apportionment factor for compliance with 10CTR20 limits for a multi-unit site. .F= the number c,t reactor units that can be operating 3-17 Rev. 10'
j
. .i l
i FWP-0-M-Oll Gaseous Effluentt' 1 l
.sinultaneously.
( 3000 mrenvyr r, j [(L'+1.lM,)0,< 3 3 (3.18) ; (X/Q), x r ! where
. .. 1 L, = skin dose factor due to beta emissions for-ident -1 uCi/h}fied ) fromnoble Tablegas3-3.
Isotope i-. (mrenvyr per M, = air. dose -factor.due to ganuna emissions for . ident uCi/m(fiednoblegasisotope1(mrad
) from Table 3-3. /yrper
-The' factor of 1.1 arenvkrad Ref. 1, page 22). converts air dose to skin dose (see The actual monitor setpoints will be adjusted for a lower ' (thus more conservative) count ; rate based on i the worst isotope release-dose rate 0 need not be changed,. except based on, reapportioning as follows and !
of allotted release fraction from , operating- i experience as mentioned above. From Table 3-3, Kr-89 ) would be . the most restrictive isotope in'~ either the i l total body or skin dose restrictions.. Assuming that- ' the total release consists of Kr-89,. the- whole body j dose equation'is more restrictive than the skin dose-equation, and the release -rate limit would- be-calculated as: i i 500 mrenvyr ry ! Q, = - (3.19) - (X/Q), x r x K, , This yields: 'i
.)
Q, = 1.39x10' pC1/sec (r,) for the stack, end 2 l Q, = vent. 3.09x10 pC1/sec (r e ) for the turbine building: i Based on maximum flow rate and. conservative' detector . efficiency, the monitor setpoints ' S, (cpm)- may be calculated as follows: 1 i S, = E,(Q,/F,) + b (3.20)
'1 3-18 . .t . 10 l
o i I 'l
'FNP-0-M-011 Gascous Effluents ,
where b = monitor background count rate (cpa) E" = gross monitor calibration factor (cpm' 3r. ; uCIAnl) r, = maximum effluent flow rate (ml/sec) Setpoint calculations will be made for radiation.
. monitors R-14, R-15, and R-22 on this basis. .he limiting release rate Q (uci/sec) is; based on the 4 valuesatisfyingthereIntionship3.17fortotalbody ,
dose. %e setpoint S t (epm) corresponding to this- > release rate may be described as . St = E,,(03 /r,) + b (3.21) where r, e maxinum release flow rate (ml/sec) 3.3.2 R.24, while not a gaseous effluent monitor, monitors an effluent release. source to the plant' vent stack, i The maximum setpoint for R-24 will be calculated based upon the monitor response curve and the alarm setpoint specified in.the 'Nehnical Specifications. S t =(E)(N;). g where '
.St = maximum monitor alarm setpoint l'n epm ~ <
r3 = gross monitor calibration factor-(cpm per pCi/cc) 4, = maxinum setpoint allowed by Technical l Specifications in.vC1/cc 1 To provide early detection and termination of an ;
. abnormally high containment purge release, the.R-24 '
setpoint may be reduced per Section d.3.1 above.. 3.3.3 R 1 monitorc the supply to d e waste gas decay tanks-from the waste gas compressor..=The. alarm setpoint. for R-13 is based on expected buildup in the waste gas system and the Technical Specification limit for waste gas storage. St = (E,) (By,) . where B = maximum expectrd buildup of radioactivity in l au pCi/cc 3-19 Rev. 8 L
- l. '
l
, MVP-0-M-011 f Gaseous Effluents l I
Noble Gas Nuclides and Dose Tactors } Nuclide Ki Li Mi .Ni . KR-83M 7.56E-02 0.00E+00 1.93E+01 2.88E+02 ! KR-85M 1.17E+03 1.46E+03 1.23E+03~ 1.97E+03 1 KR 1.61E+01 1.34E+03 1.72E+01 1.95E+03 KR-87 5.92E+03 9.73E+03 6.17E+03 1.03E+04
- KR-88 1.47E+04 2.37E+03 1.52E+04 2.93E+03 ;
KR-89 1.66E+04 1.01E+04 1.73E+04: 1.06E+04 KR-90L 1.56E+04 7.29E+03 '1.63E+04 .7.83E+03- : XE-131M. 9.15E+01 .4.76E+02 1.56E+02 1.11E+03 l XE-133M 2.51E+02 9.94E+02 3.27E+02 1.48E+03 : XE-133 2.94E+02 3.06E+02. 3;53E+02 1.05E+03 XE-135M 3.12E+03 7.11E+02 3.36E+03- 7.39E+02 ! XE-135 1.81E+03 1.86E+03 1.92E+03 2.46E+03 i XE-137 1.42E+03 1.22E+04 1.51E+03 1.27E+04 . XE=138 8.83E+03 4.13E+03 9.21E+03 4.75E+03 ; AR 8.84E+03 2.69E+03 9.30E+03 3.28E+03 j s
. These dose, factors are obtained.from Regulatory Guide 1.109 (Octopsr,1977), with uci instead of pCi. ' Units are mremryr per '
ucifs for Ki and Li, and mrad /yr per uciAn for Mi and Ni. ; i F Table 3-3. Dose Factors for Noble Gases and Daughters (Ref, Y).' 3-20 Gen. Rev. 7 L L L 1 I i' i L , 1
-- -4 , a , , -m.'.--.a
9 e
~
, INP-0-M-Oli Gaseous Effluents 3.4 CASE 00S 10CrR20 COMPLIANCE
'Ihe dose rate from each unit in unrestricted . areas due to radioactive materials released in gaseous effluents from the site C all be limited to the following expressions:
(a) Release rate limit for noble gases: p K, I [(KrQ), O ,,) i < 250 mrenvyr (3.22) [ (L, + 1.lM, ) I I (K/D), 0,,) < 1500 mrenvyr (3.23) where the terms are defined below. (b) Release rate limit 'for ,all radiciodines and for all' radioactive materials in particulate form and adionuclides (other than noble (radiciodines, gases), with half lives greate* than 8 days tritium form with half-lives gr, eater than 8 days):and all radionuclides- in particulate I, I, I, I P,, W,, 0,,) < 750 mrenvyx
.(3.24) where:
i.I = sum over all radionuclides I = sum over all vents v I = sum over all pathways P
# to en$f$ d onuclike' r due to gamma emissions'for each 3-3). " "f*8VYr Per uCi/m (Table i
q 7 q
~
l
'3-21 .Rev. 10 ,
. I
- FWP-0-M-Oll ;
Gaseous Effluents Li = the skin dose identified radionuclide,factor due in to beta. per arenvyr emissions
-uCIAnfor(Table each ,
3-3). l Mi = the air dose factor due to gansna emissions for each h identified radionuclide, in mrad /yr per uCig (Table ! 3-3), l P ' = the infant age group dose factor for the critical organ g for nuclides other than noble gasce for the inhnlation ! pathway (in units of mrenvyr per uCi/m i gnd for ground , plane and food pathways (in units of m' (mrenvyr per l uCi/sec))'. (Table 3-4) W, ,
=
(RM) for - tritium and the ' inhalation pathway and = (DM ) for other nuclides and pathways. (RM), = the highest value of the annua) average atmospheric ; dispersion- facto at the site boundary, al ' sectors, in sec . The value of 1.08ix 10'(orsec/m{ will be used for the plant vent and 4.87 x 10 secAn' for the turbine biilding stear. jet air ejector or the , ILRT vent. ' (RM),, - the highest value of the annual average atmospheric dispersion factor . at the distance of the nearest j receptor, or at 5 miles if there is no i than 5 mi1 8.03 x 10'9s, for all sectors, in sec/' . The pathway value of at less will be used for the plant vent and-8.74 X 10* see se for the turbine building steam jet air ejector or the ILRT vent. { ( bM),, - the highest value of the annual average deposition factor at the distance of the nearest receptor, or at 5 : miles if there is po pathway.atlless than 5 miles, for all ser. tors, in m' _
=
Q, , the average release rate. of.. nuclide . i 'in gaseous , effluent from each vent release point v at the site, in uCi/sec. Noble gases may be-averaged over a period of 1 hour, and any other nuclides may be averaged over a period of 1 week. , r e
}
3-22 Rev. 10 t s
- ,- - ,,, .....i,.- .*1,
- =-- .
et ,
't FNP-0-M -011 Geseous Effluents 500 = site dose rate limit for whole body in arenvyear - (
3000 = site dose rate limit'for skin in arenvyear l 1500 = site dose rate limit for any organ in.mre vyear i v i [ r
+
i i
+
l b l I t l
- i i
')
3-23 Gen. Rev. 7 ' b i
-. . _ _ . - _ . ~ . ..- . . . . ,. . .
+ FNP-0-M-011 Gaseous Effluents i Pi VALUES FOR AN INTANT Isotope Inhalation Ground Plane Cow Milk- Goat Milk H-3 6.47E+02 0.00E+00 2.38E+03 4.86E+03 P 2.03E+06 0.00E+00 1.60E+11 l 1.92E+11 i -1 CR 1.28E+04 6.65E+06 4.70E+06 5.64E+05 l MN-54 1.00E+06 1.10E+09 3.90E+07 4.68E+06 ' rE-55 8.69E+04 0.00E+00 1.35E+08 1.76E+06 FE-59~ 1.02E+06 3.89E+08- 3.92E+08 5.10E+06 co-58 7.77E+05 5.26E+08 6. 04E+07- 7.26E+06 i co-60 4.51E+06 4.40E+09 i 2.10E+08 2.52E+07 q NI-63 3.39E+05 - 0.00E+00 3.49E+10 4.19E+09 J EN-65 6.47E+05 6.88E+08 1.90E+10 '2.28E+09 j RB-86 1.90E+05 1.28E+07 2.23E+10 2.67E+09 - SR-89 2.03E+06 3.07E+04 1.26E+10 2.64E+10 SR-90 4.09E+07 0.00E+00- 1.22E+11 2.55E+11 Y-91 2.45E+06 1.51E+06 5.25E+06- 6.30E+05 ZR-95 1.75E+06 3.43E+08 8.26E+05- 9.91E+04 - NB-95 :4.79E+05 1.95E+08 2.06E+08- 2.48E+07 RU-103 5.52E+05 1.54E+08 1.05E+05. :1.27E+04 RD-106' 1.16E+07 2.99E+08 1.45E+06 1.73E+05 AG-110M 3.67E+06~ 3.13E+09 1.46E+10 1.75E+09 TE-125M. 4.47E+05 2.19E+06 1.51E+08 1.81E+07 TE-127M 1.31E+06 1.18E+05- 1.04E+09 1.24E+08 TE-129M 1.68E+06 2.82E+07 1.39E+09 I-131 1.67E+08- ' 1.48E+07 2.46E+07 1.05E+12 1.26E+12 1-133 3.56E+06 3.50E+06 9.61E+09 I-135 1.15E+10 6.96E+05 3.61E+06 2.00E+07. 2.41E+07- - CS-134 7.03E+05 2.81E+09 6.80E+10- 2.04E+11. ' CS-136 1.35E+05 2.16E+08 -5.81E+09 1.74E+10 CS-137 6.12E+05 1.15E+09 6.02E+10 1.81E+11 BA-140 1.60E+06 2.93E+07 2.412+08. 2.89E+07 CE-141 5.17E+05 1.95E+07 1.37E+07-CE-144 1.64E+06 9.84E+06 5.85E+07 1.33E+08 1.60E+07 PR-143 4.33E+05 0.00E+00 7.84E+05 -9.41E+04 ND-147 3.22E+05 1.20E+07 5.74E+05 6.88E+04< : Values are calculated from equation in ref.1, with parameters- from ref. 4. Units are arenVyr perarenvyr pera uCip'or uCi/sec per f the food andplane grou 4'for H-3 and the inhai pathways, Table 3-4. Infant Dose Factors' ! 3-24 Rev. 10 1 1 i
FNP-0-M-Oll ; Gasev,m Effluents 3.5 WASTE CAS STORAGE TANK i ( me radioactivity contained -in the waste gas decay tanks will be monitored regularly to ensure that it is below the Tech. Spec. ,
' limit of. 70,500 Curies per tank. ;
Be storage limit for each tank may, be . verified by sampling and i analysis or by use of R-13. Sample analysis results for nuclides ; other than Xe-133 will be converted to an equivalent Xe-133 level ' by normalizing with the ratia of the MPC value for that nuclide to the MPC value for Xe-133. L t 3.6 CUMULATIVE DOSE CALCULATIONS ' i luo methods of ' calculating cumulative doses can be . employed. [ These are designated " Method A" and " Method B" below. Method A - uses real-time input' of hourly averages of meteorological data, i and Method B uses highest average value of X/Q and D/Q for all : releases. Method B is the "annuti average" method described in NUREG-0133. l Method A or B may be selected at- the discretion of the licensee. l 3.6.1 Dose Calculations From Noble Gas Releases 9 I. Method At Real Time Meteorological Input The air dose in unrestricted areas due to noble gases released in gaseous effluents from each reactor at the site shall be determined by using the following expressionst During any time period, for gamma radiation:' i D, = 1.14 x 10 I, H, I at 3 I (X/Q)3 , 033, 3 (3.25) t v ' During any time period, for beta radiation:' ' D., = 1.14 x 10 E N E at I (X/Q)3,y Q, 3 3 3 j 33 (3.26) l v l where: 1.14 x 10 = l / 8760 hourF/ year 1 i. 3-25 Rev. 10 ' 1 __ , . . . . ., . ft . . . - . . - - - - -
4 TNP-0-M-011 Gaseous Effluents D, , - the total beta air dose in sector e from gaseous l effluents for the total tia period ot , in 3 mrad D, ' = the total gamma air dose in sector e from gaseous l effluents for the total time period ot , 3in mrad. l ot 3
= and the Qlengthareofaveraged the j"' time forperiod over which all gaseous releases, (X/Q)8In,- !
hours.13 For batch releases, no. time period- at shall bemorethanihour;forcontinuousreleases,botime , period ot 3shall be more than a week. , N = the g air dose identified factor due in radionuclide, to mrad beta emissions
/yr per pci/m (or(Table each- ,
3-3).. M, - the air dose factor due to gamma emissions 3for each , identified radionuclide, in_ mrad /yr per pCi/m , (Table. , 3-3). 1 (X/Q)3,, = period atthe average atmospheric dispersion factor for the time- I atthesi{eboundary,insec/m.in sector When 9, from ot is gach vent release point greater ! than 1' hour, the average shall be3 based on observations of wind speed and atmospheric stability taken at least every ' sour during At . . Q,3, = release rate . for nuclide i at hour j for vent v, in uCi/sec. II. Met. hod B: Annual Average Meteorological Input [ -l 1he dose contribution due to noble gases in gaseous effluents ; shall be calculated using the following expressions- ' For any time period, for gamma radiation: D, = 3.17 x 30" I M, I (300), 0 , 1 (3.27)- 1 i v 1 and for beta radiation: l t t 3-26 Rev 10
- l
_ - . , . . ._ =. . , _ . - - , . - - , , _ . .
~ ' FWP-0-M-011-Gaseous Effluents.
l D, = 3.17 x 10" I N, I (3D0),. Q,, (3.29) v - where , e i D, = the total gama air dose from gaseous effluents, -in mrad. ; D, = the total beta air dose from gaseous effluents, in mrad. l 3.17 x 10" = inverse of number of seconds in a year. (300), = the highest value of the annual average atmospheric ' dispersipn factor at the site boundpry, foy all sectors, i in sec/m . %e value of 1.08 x i seep 'will be used
~for the plant vent and 4.87,x 10'f sec/m for the turbine :
building steam jet air ejector. : Q ,'= the release of noble gas radionuclides, i, in gaseous i effluents in uCi for each vent. Releases shall be cumulative over the calendar month or quarter as appropriate. 3.6.2 Dose calcul<tions for radioiodines and radioactive material'in articulate form, and radionuclides (other than noble gases)=with ' 2 1f lives greater than 8 days (radiofodines, tritium, and radionuclides in particulate form with half-lives greater than 8 days). Method At Real Time Meteorological Input ~ The dose to an individual from radiciodinies, trit'um, l and ' radionuclides in particulate. form, with half lives greater than 8 days, in gaseous effluents released from each reactor at the site ]' to unrestricted areas (see rigure 5-1) shall be the following expression: For any time period t D, , , = 1.14 x 10" I, I, f p, R3py, I, ot3 I (W,3,Qi3 ,) (3.29) v k 1 3-27 Rev. 10
- , . .a , - - . . , . . . . - . , . .
. l FWP-0-M-011
; Gaseous Effluer.ts where:
1.14 x 10" = 1/8760 hours / year D,,, - the cuimilative dose from gaseous effluents.to the total l body or an organ 9 of an individual in age group a in ' sector e for the total time period Eat ,'in mrem. 3 R iPt* = the dose factor R, for each pathway p for each organ T j foreachagegroupaiornuclideiinsyctor0,in ' arenvyr per uCi/m for tritium and in m -mrenvyr per uCi/sec for other isotopes. : 2e R tvalues for each ' pathwayareasdefinedinNUREG-Olh3usingthedefault ; values of Regulatory Guide 1.109, and.are given in Table i 3-5. ne dose factors are non-zero only for nuclides-with half-lives greater than 8 days.- 1 ror sectors with real pathways within 5 miles from~the-point midway between the Unit 1 plant vent stack'and the , 1 Unit 2 plant vent stack, the values of R are used based' i on these real pathways. Forsectorswithno-real ; pathways within 5 miles from' the soint' at midway between the Unit 1 plant vent stacc and the Unit 2 plant i vent stack, E R pathways exist d the it calculated 5-mile assumina that alldistance." Refer to table 3-5, calculated in accordance with NUREC-0133. J t f,, = 1 for included pathways, O for excluded, j l W,g dose, which isdispersion parameter for calculation of food pathway .
/ J X/Q) for inhalation ?
W,p = (H-3)3l,r ( o all pathways. pathway and for tritium W,g = (D/Q)p, for other isotopes. (D/Q)g y sector =relativedepositionjareal)fortheperiodot,in e, in meters 3 ; i H 1 i
)
l. i 3-28 Rev. 10 J b
^- , , , .
[
FWP-0-M-Oll
, Gas:ous Effluents h
Maximum exposed individual
'!he maximum exposed individual is determined by selecting the age I group with the largest single organ dose (reference 7).
If 'the ground and elevated portions of the mixed mode release are ! located in separate sectors, the dose obtained is apportioned between the two sectors using the entrainment factor E. 'Ine . 3 ground portion is the fraction E, and the elevated portion is (1-E). l Method 8: Annual Average Methodology Input For any time period, organ doses from radiolodines, tritium, and. ' all radionuclides in particulate form with half-lives greater than ! c 8 days are D,,=3.17x10EERQ,'IWjQ, s i (3.30) ; ip v ; where: 3.17 x 10-' = inverse of number of seconds in a year D, , = the cumulative dose for age group a and organ T from iodines and particulates with half lives greater than 8 days in gaseous effluents, in mrem. Rip,, - the dose factor for each ragionuclide i, pathway p, organ T, and Lje group a, in m (mrenVyr) per uCi/sec-or mrenVyr per pCi/m Wy - the annual average dispersion parameter for estimating the dose. to an individual at the critical' location: i (RM) for the inhalation pathway, in sec/m', and for tritium in all a thways.3.(DM )-for the food and ground plane pathways :.n meters . ! t 3-29 Rev.-10 l l m
'. FNP-0-M-011 i Gaseous Effluents .
4 0" = the release of radiciodines, tritium, and all radioactive ! 1 materials in particulate form with half lives greater than ! 8 days, 1,.in gaseous effluents for each vent,v. Releases are cumilative over the time period' selected for the l report. The maximum exposed individual is determined by selecting the age group with the largest single organ dose (Reference 7), i i,
'l a
?
?
f i I i i
?
?
3-30 Rev. 10 1 1 I l-
FNP-0-M-011 '. Gaseous Effluents 3 1 I Pathway GROUND Nuclide. T. Body -Skin
-H-3 0.00E+00 0.00E+00 C-14. 0.00E+00 0.00E+00 P-32 0.00E+00- 0.00E+00 !
CR-51 4.66E+06 5.51E+06
.w-54 1.39E+09 1.63E+09 )
q FE-55 0.00E+00 0.00E+00- i rE-59 2.73E+08. 3.21E+08-CO-58 3.79E+08 4.44E+08- : Co-60 2.15E+10 ~2.53E+10 ~l NI-63 0.00E+00 0.00E+00 ZN-65 7.47E+08 8.59E+08-RB-86 8.99E+06' 1.03E+07 SR 2.16E+04 2.51E+04 SR-90 0.00E+00 0.00E+00 I Y-91 1.07E+06 1.21E+06 1 ZR-95 2.45E+08 2.84E+08 NB-95 1.37E+08' 1.61E+08 RU-103 1.08E+08 1.26E+08 RU-106 4.22E+08 5.07E+08 AG-110M 3.44E+09 4.01E+09 _ TE-125M 1.55E+06 2.13E+06 TE-127M 9.17t+04 1.08E+05 TE-129M 1.98E+07 2.31E+07 I-131 1.72E+07 2.09E+07 I-133 2.45E+06 2.98E+06-
'4 l
I-135 2.53E+06 2.95E+06' CS-134 i 6.86E+09 8.00E+09 CS-136 1.51E+08 1.71E+08 I CS-137 -) 1.03E+10 1.20E+10 BA-140 2.05E+07 2.35E+07 CE-141 ! 1.37E+07 1.54E+07 i CE-144 6.96Ee07 8.04E+07 PR-143 1 0.00E+00 0.00E+00 ND-147 8.39E+06 1.01E+07 i i Units are m'(arenVyr) per uC1/sec, except for tritium, in mrenVyr per uCi/sec. Table 3-5. bode Factors for Particulates and Iodines 1 3-31 - Gen. Rev. 7 ' i i 4
.-. m.-- s .n.- ,
FNP-0-M-011~ g . Gaseous Effluents l L i Pathway INHALATION Age Group: ADULT l Nuclide Bone Liver T. Body Thyroid Kidney' Lung GI-LLI l H-3 0.00E+00 1.26E+03 1.26E+03 1.26E+03 1.26E+03 1.26E+03 -1.26E+03 C-14 1.82E+04 3.41E+03- 3.41E+03 3.41E+03 3.41E+03 3.41E+03 3,41E+03 ' P-32 1.32E+06 7.71E+04 5.01E+04 0.00E+00 0.00E+00 1.00E+00 8.64E+04
- CR-51 0.00E+00 0.00E+00 1.00E+02 5.95E+01 2.28E+01 1.44E+04 3.32E+03 1 MN-54 0.00E+00 3.96E+04 6.30E+03 0.00E+00 9.84E+0; 1.40E+06 7.74E+04 .
rE-55 2.46E+04 1.70E+04 3.94E+03 0.00E+00 0.00E+00 7.21E+04 6.03E+03 FE-59 ! 1.18E+04 2.78E+04 1.06FiS4 0.00E+00 0.00E+00 1.02E+06 1.88E+05 - Co-58 0.00E+00 1.58E+03 2 0/E+03 0.00E+00 0.00E+00 9.28E+05 1.06E+05. ' Co-60 0.00E+00 1.15EA04 1.48E+04 .0.00E+00 0.00E+00 5.97E+06 2.85E+05 NI-62 4.32E+05 3.14E+0'. 1.45E+04 0.00E+00' O.00E+00 1.78E+05. 1.34E+04 i zN-65 3.24E+04 1.03E+05 4.66E+04 0.00E+00 6.90E+04 8.64E+05 5.34E+04 : RB-86 0.00E+00 1.35E+05. 5.90E+04 0.00E+00 0.00E+00 0.00E+00 1.66E+04 ! SR-89 SR-90 3.04E+05 0.00E+00 '8.72E+03 0.00E+00 0.00E+00 1.40E+06 3.50E+05 j 9.92E+07 0.00E+00 6.10E+06 0.00E+00 0.00E+00' 9.60E+06 7.22E+05 Y-91 4.62E+05 0.00E+00 1.24E+04 0.00E+00 0.00E+00 1.70E+06 3.85E+05
-ZR-95 1.07E+05 3.44E+04 2.33E+04 0.00E+00 5.42E+04 1.77E+06 .1.50E+05 NB-95 1.41E+04 7.82E+03 4.21E+03 0,00E+00 7.74E+03 5.05E+05 1.04E+05 RU-103 (
1.53E+03 0.00E+00 6.58E+02 0.00E+00 5.83E+03 '5.05E+05 1.10E+0c ; RU-106 6.91E+04 0.00E+00 8.72E+03 0.00E+00 1.34E+05 9.36E+06. 9.12E+ AG-110M 1.08E+04 1.00E+00 5.94E+03 0.00E+00 1.97E+04 4.63E+06 3.02E+v, , TE-125M 3.42E+03 1.58E+03 4.67E+02 1.05E+03 1.24E+04 '3.14E+05 7.06E+04' TE-127M 1.26E+04 5.*i7E+03 1.57E+03 3.29E+03- 4.58E+04 9.60E+05 .1.50E+05 TE-129M I-131 9.76E+03 4.67E+03 .1.58E+03 3.44E+03 3.66E+04 1.16E+06 3.83E+05 I-133 2.52E+04 3.58E+04- 2.05E+04 1.19E+07 6.13E+04 0.00E+00 6.28E+03 8.64E+03 1.48E+04 4.52E+03 2.15E+06 2.58E+04 0.00E+00 8.88E+03 . I-135 2.68E+03 6.98E+03 2.57E+03. 4.48E+05 1.11E+04 .0.00E+00 5.25E+03 CS-134 3.73E+05 8.48E+05 7.28E+05 0.00E+00 2.87E+05 9.76E+04' 1.04E+04 CS-136 CS-137 3.90E+04 1.46E+05 1.10E+05 0.00E+00 .8.56E+04 1.20E+04 1.17E+04 - 4.78E+05 6.21E+05 4.28E+05 0.00E+00 2'22E+05 7,52E+04 8.40E+03 BA-140 3.90E+04 4.90E+01; 2.57E+03 0.00E+00 1.67E+01. 1.27E+06 2.18E+05 , CE-141 CE-144 1.99E+04 1.35E+04 1.53E+03 0.00E+00 6.26E+03 3.62E+05. 1.20E+05 i PR-143 3.43E+06 1.43E+06. 1.84E+05 0.00E+00 8.48E+05 7.78E+06 8.16t+05 ND-147 9.36E+03 3.75E+03 4.64E+02' O.00E+00- 2.16E+03 2.81E+05 2.00E+05 a 5.27E+03 6.10E+03 3.65E+02 0.00E+00 3.56E+03; 2.21E+05 1.73E+05- ( Units are m* (mrenVyr) per uCi/sec, .except for tritium, in mrenVyr per uCi/sec. Table 3-5.. Dose ractorn for Particulates and Iodined i 3-32 Gen. Rev. 7 1 t
g .: ,: , 7 j v. % a t
'FNP-0-M-011 1
[ f. Gaseous Effluents Pathway: INHMATION . Age Group:- TEEN Nuclide Bone Liver T. Body Thyroid. Kidney Lung'- .- GI-LLI 1 H-3 0.00E+00 l.27E+03 1.27E+03 l'.27E+03 1;27E+03.l1.27E+03? 1.27E+03' H C-14 P 2.60E+0444.87E+03 - 4.87E+03 4.87E+03 4.87E+03 4.87E+03 4.87E+03 - CR 1.89E+06 : 1.10E+05 .' 7.16E+04 0.00E+00 = 0.00E+00 . 0.00E+00. 9.28E+04 - T I 0.00E+00 0.00E+00 = 1.35E+02. E7.50E+01'- 3.07E+012.2.10E+04' 3.00E+03'
~
h 54 0.00E+00 5.11E+04 8.40E+03.-0.00E+00 1.27E404 -1 98E+06 .6.68E+04 .
'FE-55
'FE-59 3.34E+04 2.38E+04' 5.54E+03^ 0.00E+00 0.00E+00 1.24E+05- 6.39E+03-co '1.59E+04 0.00k,# - -3.70E+04 -1.43E+04 0.00E+00 0.00E+00 1.53E+06 1.78E+05 1 1 1
Co-60 3 2. 0~'E+03 : 2.78E+03: 0.00E+00' O.00E+00'L1.34E+06: 9.52E+04 1 NI-63 0.00E+0C .1.517+04- 1.98E+04 0.00E+00 'O.00E+00 8.72E+06 2.5?E+05' !- 5.80E+05 4.34E+04 1.98E+04 : 0.00E+00' O 00E+00? 3.07E+05; L1.42E+04 LZN-65' ~ h 86 3.86E+04( 1.343+05 . 6.24t+04 ' O.00E+00 ' 8.64E+04 : 1.24E+06 4.66E+04 l
-0.00E+00_ 1.90E+05; 8.40E+04 0.00E+00 'O.00E+00 0.00E+00' 1.77E+04 SR-89~ 4,34E+05. 0.00E+00 1.25E+04 .0.00E+00 0.00E+002 2.42E+06' 3.71E+05 - i i
SR 1.08E+08 ' 0;00E+00' '6.68E+06 ? ' O.00E+00 : 0.00E+00 1.65E+07 1 7.65E+05 Y-91'- 6.61E+05 0.00E+00 1 77E+04 0.00E+00 . 0.'00E+00. 2.94E4 06; ,4.09E+05 - ZR-95 , ' NB -1.46E+05 '4.58E+04' 3.15E+04 0.00E+00-i6.'74E+04~-2.69E+06 l'49E+05 1.86E+04 1.03E+04. 5.66E+03 0.00E+00--1.00E+04 17.51E+05L -9.68E+04 RU-103' -2.10E+03 0.00E+00 8.96E+02 10.00E+00 17,43r:+03=~7.83E+05 'liO9E+05 RU-106 9.84E+04 0.00E+001.24E+04:-'0.00E+00 1.90E+05' 1.61E+07 9.60E+05 l AG-110M '1.3BE+04 -1.31E+047.99E+03' 0.00E+00. 2.50E+04 6.75E+06 J2.73E+05 i TE-125M 4.8BE+03 2.24E+03 6.67Ev02: 11.40E+03 0;00E+00 5.36E+05 7.50E+04- d TE-127M =1.80E+04 8.16E+03! 2.18E+03J 4.38E+03' 6.54E+041.6(E+06~ 1.59E+05 i TE-129M' I-131 1.39E+04 6.58E+03 -2.25E+03a 4.58E+03 5.19E+04L 1.98E+06: 4.'05E+05 i I-133 3.54E+04 4.91E+04- 2.64E+04- 1;46E+07 8.40E+04 0.00E+00 6.49E+03- ' 1.22E+04 2.05E+04, 6.22E+03 2;92E+06: 3.59E+04. 0.00E+00-.1.03E+04 ! I-135 3.70E+03 9.44E+03 3.49E+03 C CS-134 A54L1.'49E+04 -0.00E+00 '6.95E+03 5.02E+05 1.13E406' 5.49E+05 0.0% - 3 ;75E+05: '1'.46E+05 . 9.76E+03 - CS-136- 1 CS-137 5.-15E+04 1.94E+05- 1.37E+05 0.00E+w '1.10E+05 1.78E+04 1.09E+04 f BA-140 6.70E+05' 8.48E+05 3.11E+05 0.00E+00 3.04E+05 1.21E+05 8.'48E+03 - 5.47E+04' 6.70E+01 3.52E+03;_0.00E+00 ;2;28E+01( '2.03E+06 -2.29E+05 U
'I
=
CE-141 N" CE-144 2.84E+04 1.90E+04! 2.17E+03 0.00E+00? 8.88E+03L 6.14E+05 1.26E+05-M-143 4.89E+06 2.02E+06 12.62E+05 - 0.00E+00 1.21E+06 ' ' 1.34::+07 ' 8.64E+05 i
- 1.34E+04 5.31E+03 6.62EA021 0.00E+00--3;09E+03) 4.83E+05 2.'14E+05' !
, No-147 7.86E+03 8.56E+03 5.13E+02- 0.00E+00 5.02E+03 l3.72E+05 1.82E+05' k's A
Units are - m'(mrenVyr) per =uci/sec, except for tritium, in mrer.Tr per uCi/sec. Table 3-5. Dose Factors fvr Particulates and Iodines L3-33 Gen.,Rev. ' l e j
, _Q
.~ + ,
r FNP-0-M-011 l Gaseous Effluents: - C 1athway: INHAIATION ' Age Group: CHILD. . Nuclide b_ 1 Liver T. Body T_hgroid: Kidney Lung GI-LLI-i
'H 2
-C-14 0.00E+00 1.12E+03. 1.12E+03 fl.12E+03 -1.12E+03 1.12E+03 =1.12E+03 '
0 P-32 3.59E+04 6.73E+03! 6.73E+03 6.73E+03l 6.73E+03-.6.73E+03: 6.73E+03' 2.60E+06- 1.14E+05 9.80E+04 '0.00E+0010.00E+002 0.00E+00 '4.' 22E+04 ; CR-51"
- MN-54 0.00r+00 0.00E+00 --1.54EF02 8.55E+01' 2.43E+01~ : 1.70E+04 - l'.08E+03 - E 0.00E+00' 4.29E+04 9.51E+03?;0.00E+00~ 1.00E+04 -1.58E+06 t2.29E+04-FE-55' rE 4.74E+04 2.32E+04 7.7 e+03 'O 00E+00 0.00E+001.11E+05'+2!87E+03!
Co-58 2.07E+04 3.34E+04 c1.672+04' 0.00E+00 0.00E+00- 1.27E+06- 7.07E+04' 1
- 0. 00E+00.. I'.77E+03 ;3.16E+03:.0.00E+00- O.00E+00.'.1.11E+06 -3.44E+04 1 Co-60..
NI-63 0.00E+00 il'.31E+04 2.26E+04. 0.57E+00 0.00E+007.07E+06 i9.62E+04-8.21E+05':4.63E+04 2.80E+04 0.00E+00 0.00E+00m.2.75E+05 :6.~33E+03< l ZN-65 RB-86 4.26E+04-.1.13E+05 '7.03E+04 6.J0E+00: 7.14E+04 9.'95E+05 .1.63E+04. '! 0.00E+00 1.98E+05 11'.14E+05 0.00E+00 0.00E+00 10.00E+00;'7.99E+03 ; SR-89 SR-90 5.99E+05 0.00E+00: 21.72E+04 :0.00E+00 0400E+00. 2.16E+06s l'.675+05l t
.Y-91 1.01E+08 0.00E+00 6.44E+06 0.00Eo00.- 0.00E+00 1248E+07. 3.43E+05
'9.14E+05 0.00E+00 2.44E+04 0.00E+00' O.00E+00 "2.63E+06 ,1.84E+05- :
ZR-95 .! NB-95 1.90E+05 4.18E+04: 3.70E+04 0.00E+00 5<96E+04 '2.23E406. 6.21E+04- ~f 2.35E+04 9.18E+03 :6.55E+03';0.00E+008.62E+03. 6.14E+05? 3.70E+04' 1 RU-103 2.79E+G3'-0.00E+00 1,07E+03;=0.00E+00 7.=03E+03. 6.62E+05 l4.48E+04' RU-106 1.36E+05 0.00E+00 1.69E+041 0.00E+00- 1.84E+05 J1.43E+07 E4229E+05 - AG-110M' 1.69E+041 l'.14E+04 9.14E+03 ,0.00E+00. 2.12E404' 5.48E+06' 1 00E+05- -
. 1
'n:-125M 6.73E+03 2.33E+" 9.14E+02 '1!92E+03 0.00E+00' 4.77E+05? 3.38E+04- R TE-127M 2.49E'04 .8.5 h 03 3.02E+03 6.07E+03 6.36E+04 L1'48Es06 17.14E+04' .
TE-129M I-131 1.92E+04- S.85E+03 3.04E+031 6.33E+03 5.03E+04 1.76E+06 1.82E+05-I-133. 4.81E+04 4.81E+04 2.73E+04 L1.62E+07 '7.88E+04..D.00E+001 2.845:+03 1 1.66E+04 2.03E+04 7.70E+03 3.85E+06 3.38E+04 1 0.003+00 5.48E+03: I-135 4.92E+03 8.73E+03 CS-134 4.14E+03-~7-92E+05~ l.34E+041 0.00E+001-4.44E+034 6.51E+05 3.01E+06. 2.25E435' O.00E+00 .3;30E+05 1.21E+05 '~3.85E+03 D CS-136 6.51E+04 , p 1.71E+05 1,16E+05 - 0.00E+00 :3 9.55E+04 { l1' 45E+04 : 4.18E+03 y CS-137 .
; BA-140 9.07E+05 8 25E+05 1.28E+05_.0.00E+00- 2.82E+05l'1.04E+05 J3.59E+03 i
'7.40E+04 6.48E+01- 4'33E+03y0.00E+00 2.11E+01o-1'.74E+06' 1.02E+05-1 CE-141-CE-144 3.92E+04H 1.95E+041 2.90E+03 0.00E+00' 8.55E+03 5.44E+05. Si66E+04
-6.770+06 2.12E+06 ' 3.61E+05 : 0.00E+00 ' ,1.17E+06 .1.20E+07 ; 3.89E+05 1 PR-143-NL-147 1.85E+04 1.08E+04 5.55E+03! 9.14E+02. 0.00E+00 3.00E+03 4.33E+05 9.73E+04
/
8.*13E+03' 6.81E+02 0.00E+00' 4.'81E+03. 3.28E+058'.21E+04 h H Units are m*(mrewyr) per uCi/sec, except forL tritium, in mrenVyr per uC1/sec. i
, 8 Table 3-5. Dose Factors'for Particulates and Iodines .
q ..- 3-34 i Gen. Rev.17-2 l
] -
, s t
t
\ U 4
- (I '
$ L,;n. : . - . . . ,, . La- a-+- ~ ~ T - " " ~ " ~ *' ~~
L) 5
. i
. Gblous; Effluents ~
)
. Pathway: INHALATION -Age vroup:;; INFANT? 3 Nuclide~' Bone Liver ~T. Body ' Ihyroid !
Kidney Lung GI-LLI. e 1
'H-3 0;00E+00 6.47E+02 6.'47E+02 .6.47E+02. 6.47E+02: 6.47E+02L 6.47E+02 i
C 1 2.65E+04- 5.31E+03J 5,31E+03 15.31E+03 5.31E+03 5.31E+03. 5.31E+03' " P'R3 L2.03E+06 '1.12E+05 7.74E+04!,0.00E+00 0.00E+00 ~0.00E+00' 1'.61E+04 :
' CR41 '
MN-54 .0.00E+00- 0.00E+00 8.95E+01 5.75E+01'.I'32E+01L 1.28E+04 -3.57E+02 C 0.00E+00 2.53E+04 '4.98E+03:.0.00E+00" 4.98E+03 1.00E+06s:7.06 D03'
'FE-55 1-97E+04=<1.17E+04 3.33E+03 0100E+00I0.0bE+00h8.'69E+04J1'.09E+03, 1FE-59 1.36E+04i 2.35E+04 9.48E+03. 0.00E+00. 0.00E+00 1.02E+0612,48E+04; CO -58 L i!
0;00E+00' 1.22E+03 1.82E+03 0.00E+00 -0.00E+00.47.77E+05 /1.11E+04- ' co-60 -0.00E+00 8.02E+03; 1.18E+04 (0.00E+00 0.00E+00 4.51E+06 3.19E+04 NI-63', 3.39E+05 2.04E+04 / l1.16E+04 E 0.00E+00! 0;00E+00- 2.09E+05 ; 2.42E+03, ZN -1.93E+04. 6.26E+01 RB-86 s0.00E+00 3.11E+04 1.90E+05E8.82E+04l[0.00E+00s0;00E+00' 3'.'25E+04J'6.47E+ i 1 SR-49 0.00E+00 0.00E+00 !3.04E+034 SR-90~ m3.98E+05 ~0.00E+00 1.14h04 0.00E+00 0.00E+00' 2.03E+06'16.40E+04' 4.09E+07: 0.00E+00:L2.39E+06'-0.00E+001 0.00E+00 1.12E+07! 11.31E+05; A Y-91 5.88E+05 0.00E+00' :1.57E+04 0.00E+00 i 0.~00E+00 : 2;45E+06' 7.03E+041
-ZR-95 1 3
1.15E+05 2.79E+04. 0.03E+04 ~0.00E+00 '3.11E+04 1'.75E+06 ' : 2.17E+04 . NB-95 1.57E+04 6.43E+03 3.78E+03 0~00E+00' 4.72E+03' 4.79E+05D1.27E+04
.RU-103 .2.02E+03 0.00E+00 6.79E+02' O 00E+00 ; 4.24E+03? . 5.52E+05 M 1.61E+04 n
RU-106- 8.68E+04 .0-00E+00 1.09E+04. 0.00E+00 ; 1.07E+051 ~ 1'.16E+07 : - 1.64E+05 - AG-110M 9.98E+03 7.22E+03= 5.00E+03; 0.00E+00F 1.09E+04 '3.67E+06 i3.3.0E+04i e I TE-125M 4.76E+03 1.99E+03 6'.58E+02 l1.62E+03 .0.00E+00. 4.47E+05-11.29E+04: ~ s TE-127M 1.67E+04 '6.90E+03 ~2.07E+03 4.87E+03 3.75E+04 1.31E+06'!2;73E+042 3 ' TE-129M I-131 -1.41E+04 6.0?E+03 2.23E+03. 5.47E+03 a3.18E+041 l'.68E+06c 6.90E+04" I-133 3.79E+04 ;4.44E+04 1.96E+04 :1.48E+071: 5.18E+04c 0.00E+00:01.06E+03. , I 1.32E+04 '1.92E+04 S.60E+03 '3.56E+06'!2.24E+04 0.00E+00;4 2.16E+03-
- 4 I-135 CS-134 3.86E+03 ' 7.63E+03 2.77E+03i L 6.'96E+05I 8.47E+03! 0:00E+00 1.83E+03: a CS-136 3.96E+05; 7.03E+05 7.45E+04: 0.'00E+00i 1.90E+05U7.97E+04El'.33E+03 Y4 CS-137 4.83E+04.'i.35E+05: -5.29F+04i O.'00E+00. 6.64E+04! 1.18E+04 il.'43E+03~
L BA-140 5.49E&055.60E4G1 5.60E404 6.12E+05f2.90E+ 4.55E+04 0.~00E+00 'I'.72E+05$ 7113E+04 $1.33E+03' 3 x 0.00E+00-J1;34E+014'1'60E+06: 3.84E+04 H CE-141 2.77E+04. 5. 67E+04'11.99E+03 0.00E+00 15;25E+03 :Sil7E+05 ;2.16E+04 ~ CE-144 3.19E+06 1. 21E+06 :1.76E+05 : .0.00E+00 : 5;38E+05 L 9.84E+06 C l'.48E+05 - PR-143 1.40s+04 !5.24E+03 ND-147 6.99E+02<.040?E+00 1.97E+03 J4.33E+051 3'.72E+04 ,a i 7.34E G '8.13E+03 5.00E+02 -0.00E+00 13.15E+03: 3.22E+05 3.12E+04 Units are area /yr per uCi/sec
,j 3 0 d
Table' 3-5. Dose Factors for Particulates and -Iodiness (' Continued)" , 3-35 . Gen. Rev. 7 >
' .3 y;
6m , d.
'l
, d
~
, , e .2
.f - - - ' ^ ' ~;
~^- ' ~- '
4 ~, j .
- ~ - , ., , E o w .. , ;l
\ J .
' FNP-0-M-011 l t #,
l Gaseous Effluents l u
- l1 4 j Pathwayt'. CON MILK A9e' Group: ADULTJ ' *
- l. Nuclide Bone' : Liver T. Body- . Thyroid- Kidne? Lung: GI-LLI' I!
i :H 0.00E+00' 7.63E+02 7.63E+02 .7.63E+02 7.63Ed2 '7.63E+02.17.63E+02 C-14 2.63E+08 ;5.27E+075.27E+07 5.27E+07: 5.27E+0 5.27E+07< 5.27E+07 ! E P 1.71E+10. l'06E+09 6.61E+08 'O.00E+00' O.00E+00 0.00E+00. 1.92E+09< 2 CR 0.00E+00 0.00E+00 2.86E+04 1.71E+04 6.30E+03 '3.79E+04' 7.19E+06 ) i ' f MN-54 0.00E+00 8.41E+06: 1.61E+06 0.00E+00 2.50E+06 c0.00E+00- 2.58E+07 L
.FE-55: 2,51E+07 1.74E+07~.4.05E+06. 0.00E+00: 0.'00E+00 9.68E+ob. 9.95E+06 j FF-59 2.97E+07 6.98E+07 2.68E+07.- 0.00E+001 0.00E+001.95E+07 2.33E+08L
- - 1 Co-50 0.00E+00 :4.71E+06: 1.06E+07 0.00E+00 0.00E+00 .0.00E+00 <9.55E+07. I Co-60 0.00ii;+00 1.64E+07 3.62E+07 0.00E+00 0.00E+00 0.00E+00 3,08E+08 (
-NI -6.73E+09' 4.66E+08- 2.26E+0BO 00E+00' O.00E+00~'O.00E+001'9;73E+07' ZN-65 '1.37E+09 ~4.37E+09' 1.97E+09 0.00E+00 2.92E+09,;0.00E+00:'2.75E+09, RS-85 0.00E+002.60E+09 '1.21E+09 0.00E+00 0.00E+00 ;0.00E+00 5.12E+08' 1 S".-89 1.45E+09 0.00E+00 4.16E+07 0.00E+00 4 0.00E+00 -0.00E+001 2.33E+08 1 SR-90 4.68E+10 ~0.00E+00: 1.'15E+10 0.00E+00 0.00E+00 0.00E+00 E1.35E+09' l Y -91 8.59E+03 0'.00E+00. 2.30E+02 0.00E+00' 0.00E+00L 0.00E+00. 4-73E+06: .
ZR-95 9.43E+02 3.03E+02 2.05E+02 0.00E+00 4.75E+02z 0.00E+00 9.59E+05-NB-95 8.26E+04 4.59E+04. 2.47E+04 0.00E+00 4.54E+04 .0.00E+00. 2.79E+08 RU-103 'l.02E+03= 0.00E+00 4.39E+02 0.00E+00 3.89E+03 c0;00E+00 '1.19E+05 RU-106 2.04E+04. 0.00E+00 :2.58E+03 0.00E+00 3;94E+04: 10.00E+00;:1;32E+06' AG-110M 5.82E+07 5.39E+07- 3.20E+07 0.00E+00 1.06E+08'i0.00E+00 ~2.20E+10 l TE-125M 1.63E+07 5.90E+06 2.18E+06 4.90E+06- 6.63E+07: MO 6.50E+07- ; TE-127M 4.58E+07 1.64E+07 5.58E+06 1.17t+07 '1.86E+08 0.005+00 1.54E+08 1 TE-129M 6.02E+07 2.25E+07- 9.53E+06 2.07E+07 2.51E+08 0.00E+00 -3;03s+08 ' I-131. 2.96E+08 4.14E+08 2.43E+08 1.39E+11 ~ 2GE+v8 .0.00E+00 1.12E+08 I-133 3.87E+06 6 '.3E+06 '2 SE+06: 9.90E+08 : 1.18E+37.10.00E+00' 6,05E+06 I-135 1.29E+04 3..lE+04 1.24E+04 ~2.22E+06 45.40E+04'LO.00E+00 i 3.80E+04 CS-134- '5.65E+09 1.35E+13 '1.10E+10- 0.00E+00a 4.35E+09: l'.45E+09 2.35E+08 CS-136 2.63E+08 .1.04E+09 7.48E+08: 0.00E+00 (5.78E+08 7.93E+07 : -1.3 8E+08 CS-137. 7.38E+09 '1.01E+10. 6.61E+09 -0.00E+00? 3.43Et09 1.14E+09- 1.95E+08-BA-140 5 2.69E+07 3.38E+04z 1.76E+06 .0.00E+00 1.15E+04L:1.93E+04 5.54E+07- 4 CE-141 4.84E+03 3.28E+03 3.72E+02 0.~00E+00 1.52E+03 LO 00E+00 E1.25E+07 0 CE-144 3.58E+05 ~1.50E+05 1.92E+04 0.00E+00' 8.87E+04 0.00E+0011.21E+08. PR-143 sy l'.58E+02 !6.33E+01- 7.83E+00 -0.'00E+00 3.66E+01';0.00E+001 6.92E+05- ' ND-147 9.42E+01 .1.C9E+02 6.51E+00 0.00E+00'.6.36E+01E.0.00E+00; 5.22E+05 Units are m'(mres/yr) .per uCi/sec, except forf tritium, in-mrenVyr
. per uCi/sec. a Table 3-5.4 Dose Factors for Particulates and Iodines.
3-36~ LGen.'Rev. 7- < l, . E j i . s t
, j.,
4 a i
, q g 4i ;' [h! ,[
FNP-0-:1-011 Gaseous Effluents Pathway: cod MILK Age Group: TEEN Nuclide Bone Liver T,. Body Thyroid Kidney Lung GI-LLI H-3 C-14 0.00E+00 9.94E+02 9.94E+02 9.94E+02 9.94E+02 9.94E+02 9.94E+02 P-32 4.86E+08 9.72E+07 9.72E+07 9.72E+07 9.72E+07 9.72E+07 9.72E+07 CR-51 3.16E+10 1.96E+09 1.22E+09 0.00E+00 0.00E+00 0.00E+00 2.65E+09 MN-54 0.00E+00 0.00E+00 4.99E+04 2.77E+04 1.09E+04 7.13E+04 8.39E+06 0.00E+00 1.40E+07 2.78E+06 0.00E+00 4.18E+06 0.00E+00 2.87E+07 rE-55 ~ FE-59 4.45E+07 3.15E+07 7.36E+06 0.00E+00 0.00E+00 2.00E+07 1.37E+07 Co-58 5.18E+07 1.21E+08 4.67E+07 0.00E+00 0.00E+00 3.81E+07 2.86E+08 Co-60 0.00E+00 7.94E+06 1.83E+07 0.00E+00 0.00E+00 0.00E+00 1.09E+08 NI-63 0.00E+00 2.78E+07 6.26E+07 0.00E+00 0.00E+00 0.00n+00 3.62E+06 1.18E+10 8.35E+08 4.01E+08 0.00E+00 0.00E+00 0.00E+00 1.33E+08 l-ZN-65 RB-86 2.11E+09 0.00E+00 7.32E+09 4.7' 'o 3.41E+09 0.00E+00 4.68E+09 0.00E+00 3.10E+09 SR-89 2.67E+09 0.0 2.22E+09 0.00E+00 0.00E+00 0.00E+00 7.00E+08 SR-90 6.61E+10 0f 7.66E+07 0.00E+00 0.00E+00 0.00E+00 3.19E+08 a 1.63E+10 .00E+00 0.00E+00 0.00E+00 1.86E+09 Y-91 1.58E+04 0. vs a,00 4.24E+02 0.00E+00 0.00E+00 0.00E+00 6.48E+06 ZR-95 NB-95 1.65E+03 5.21E+02 3.58E+02 0.00E+00 7.65E+02 0.00E+00 1.20E+06 RU-103 1.41E+05 7.81E+04 4.30E+04 0.00E+00 7.57E+04 0.00E+00 3.34E+08 RU-106 1.81E+03 0.00E+00 7.74E+02 0.00E+00 6.38E+03 0.00E+00 1.51E+05 3.75E+04 0.00E+00 4.73E+03 0.00E+00 7.24E+04 0.00E+00 1.80E+06 AG-110M 9.63E+07 9.11E+07 5.5(E+07 0.00E+00 1.74E+08 0.00E+00 2.56E+10 TE-125M 3.00E+07 1.08E+0'i 4.02E+06 8.39E+06 0.00E+00 0.00E+00 8.86E+07 TE-127M B.44E+07 2.99E+07 1.00E+07 2.01E+07 3.42E+08 0.00E+00 2.10E+08 1E .29M 1.10E+08 4.09E+07 1.74E+07 3.55E+07 4.61E+08 0.00E+00 4.13E+08 I-131 I-133 5.377+08 7.52E+08 4.04E+08 2.20E+11 1.30E+09 0.00E+00 1.49E+08 7.07E+06 1.20E+07 3.66E+06 1.67Ev09 2.10E+07 0.00E+00 9.00E+06 I-135 2.28E+04 5.88E+0' CS-134 2.18E+04 3.78E+06 9.28E+04 0.00E+00 6.51E+04 CS-136 9.82E+09 2.31E+10 1.07E+10 0.00E+00 7.34E+09 2.80E+09 2.87E+08 CS-137 4.40E+08 1.76E+09 1.18E+09 0.00E+00 9.60E+08 1.51E+08 1.42E+08 BA-140 1.34E+10 1.78E+10 6.20E+09 0.00E+00 6.06E+09 2.35E+09 2.53E+08 4.85E+07 5.95E+04 3.13E+06 0.00E+00 2.02E+04 4.00E+04 7.48E+07 CE-141 CE-144 8.88E+03 5.93E+03 6 81E+02 0.00E+00 2.79E+03 0.00E+00 1.70E+07 PR-143 6.58E+05 2.72E+05 3.54E+04 0.00E+00 1.63E+05 0.00E+00 1.66E+08 ND-147 2.90E+02 1.16E+02 1.44E+01 0.00c+00 6.73E+01 0.00E+00 9.55E+05 1.81E+02 1.97E+02 1.18E+01 0.00E+00 1.16E+02 0.00E+00 7.11E+05 Units are m* (mrenVyr) per uCi/sec, except for tritium, in mrenVyr per uCi/sec. Table 3-5. Dose Factors for Particulates and Iodines 3-37 Gen. Rev. 7 l l _ a . -
e Q q FNP-0-M-011 y Gaseous Effluents n i Pathway CCW MILK Age Group: CHILD
'gelide' Bone Liver T. Body- Thyroid -Kidney. Lung- GI-LLI~
H-3 ' E C 0.00E+00 '1.57E+03 :l'57E+03 1.57E+03 1.57E+0? 1.57E403 L1.57E+03 1.19E+09 2,39E+08 2,39E+08 2.39E+08 12.39E+08 2.39E+08 s2.39E+08 _; P 17,78E+10 3.64E+09 -3,00E+09. 0.00E+00 0.00E+00 -0.00E+00 2.15E+09 CR-51 i MN-54
~0.00E+00 0.00E+00- 1.02E+05 5.65E+04: 1.54E+04~Ll~.03E+05 5.40E+06 !
0.00E+00: 2.10E+07 5.59E+06' O.00E+005.88E+06 0.00E+00 1.76E+07 l FE-55 1~.12E+08. 5.93E+07 1.84E+07 0.00E+00 0;00E+00 3.h5E+07.1.10E+07 FE-59 Co-58 1.20E+08 1.95E+08: 9.69E+07: 0.00E+00.-'O.00E+00 5.64E+07 2.03E+08 0.00E+00- l'.21E+07 3.71E+07- 0.00E+00; 0.00E+00 0.00E+00 7.07E+07 CO-60
-NI-63 0.00E+00 4'.32E+07 ti.27E+08 0.00E400 10.00E+00' O.00E+00 2.39E+08:
2.96E+10 1.59E+09 '1.01E+09 .0.002+00 :0.'00E+00 10.00E+00 1.07E+08-ZN-65 Rh-86 4.13E+09 1.10E+10 6.85E+09 0.00E+00 6'94E+09 0.00E+00- 1.93E+09 l 0.00E+00 8;77E+09' 5;39E+09 -0.00E+00< 0.00E+00 0.00E+00 5.64E+08 SR-89: '6.62E+09 0'.00E+00J1.89E+084 0.00E+00'LO.00E+00 ;0.00E+00 '2.56E+08 , SR-90 -l'.12E+11 0.00E+00. 2.83E+F 'O.00E+00"0.00E+00: 0.00E+00--1,51E+09 a Y 3 =.90E+04 - 0.00E+00 1.04! +0; 0.00E+00 3. O',E+00 ' O.00E+00 5.20E+06 ZR NB-95 3.83E+03' 8.42E+02- 7.50E+02 0.00E+00 1.21E+031~0.00E+00 '8.79E+05 3.18E+05 'l'.24E+05 8.84E+04 ,0.00E+00 ~1.16E+05 0.00E+001 2.29E+08 RU-103
.RU-106 4.28E+03 0.00E+00 :1.65E+03 '0.00E+00 11.08E+04:!0.00E+00: 1.11E+05 a 9.24E+04 0.00E+00- 1.15E+04::0.00E+00 :1.25E405;'O.00E+001.44E+06 AG-110M 2.09E+08 l'.41E+08 :1.13E+08 0.00E+00 2.63E+084 0.00E+00;J1.68E+10 '
TE-125M 7.38E+07 2.00E+07 9.84E+06 2.07E+07 ~0.00E+00::0.00E+00 :7.12E+07- j TE-127M 2.08E+08 5.60E+073 2.47E+07 4.97E+07 ; 5.93E+n 0.00E+00 M1.68E+08-- ; TE-129M 2.71E+08 7.58E+07, 4.21E+07 8.75E+07' 7.97E+08E i0.00E+00' 3.31E+08 I-131 1.30E+09 1.31E+09. 7.45E+08z 4.33E+11 ;2.15E+09O.00E+00 11.17E+08- -- { I-133-1.72E+07 2.12E+07 '8.04E+06: 3.h E+09 .3.54E+07= 0.00E+00 J8.56E+06- s a I-135 5.41E+04 9.73E+04 .4.60E+04; 8.62E+06 1.49E+05 0.00E+001.7.41E+04 CS-134- ' CS-136 2.26E+10 3.72E+10 7.84E+09 10.00E+00'11215E+10 4.13E+09 '2.00E+08-
'CS-137: 1.01E+09 2.78E+09 1.80E+09' O.00E+00 ali48E+09 .2.21E+08 9.77E+07 i BA-140 3.22E+10 3.09E+10 4.55E+09 0.00E+007 1'.01E+10s 3.62E+091 1293E+08 i 1.17E+08 '1.03E+05 6.84E+06 0.00E+00 3.'34E+04 :6'.12E+04 5.93E+07 CE-141 . . ~
z . O CE-144 2.19E+04 1.09E+04 -1.62E+03 0.00E+001 4.78E+03 0.00E+00 - l'.36E+07 h 1.62E+06 5.09E+05 8.66E+04 'O.00E+00, 2.82E+05 0.00E+00' l.'33E+08 PR-143' - ND-147 7.18E+02 2.16E+02' 3.56E+01 0.00E+00-?1.17E+02 10.00E+00 7.75E+05 j 4.45E+02 3.60E+02 2.79E+01 0.00E+00 1.98E+02 0.00E+00(;5.71E+05? 1 1, Units per < are m* (mrenVyr) perluci/sec,; except for tritium, in mrenVyr uCi/sec. 1
, Table 3-5. Dose Factors for Particulates and Iodinesi '
3-38 Gen. Rev.L7 { . a 1 o ,
- (
>t.3
_ yp, . r . 48 - I: - 5 's
4. r k: q FWP-0-M-011 i
?1
, Gaseous Eff1'Jents
{
, a Pathway CON MILK LAge Groups INEANT Nuclide Bone' Liver T. Body Thyroid ' Kidney- Lung ~GI LLI i
H-3 It C-14 0.00E+00 2.38E+03 2.38E+03 2.38E+03 . 2.38E+03. 2.38E+03 2.38E+03 L 2.34E+09 -5.00E+08 5.00E+08 5.00E+081 5.00E+08. 5.00E+08 5.00E+08,
'P-32 :1.60E+11 9.43E+09' 6.22E+09 0.00E+00 ,0.00E+00- 0.00E+00 '2.'17E+09-CR-51
<MN-54 0.00E+00 0.00E+00 :1.61E+05 1.05E+05 2.30E+04 2.05E+05 -4.70E+06. 3
'0.00E+00 i3.90E+071 8.84E+06 0.00E+00 18.64E+06' O.00E+00 1.43E+07 H
o TE-55: e TE-591
'1.35E+08 ~8.73E+07 -2.33E+07.-0.00E+001 0.00E+00- 4.27E+07. 1.11E+07 '
CO-5S i ~ 2.24E+08 -3.92E+08 11.54E+08 ~ - 0.00E+00 0.00E+00 : 1.16E+08 ~ 1.87E+08 : Co 0.00E+00 2.42E+07 6.05E+07 0.00E+00' O.00E+00 0.00E+001 6.04E+07' 1 NI-63 0.00E+00c 8.82E+07 '2.08E+08- 0.00E+00 0.00E+00. 0.00E+001 2.10E+08~ J 3.49E+10 2.16E+09- 1.21E+09 0.00E+00- 0.00E+00 c0.00E+00 ;1.07E+08' 1 ZN ' 5.55E+09 .1.90E+10 l8'.78E+09' 0.00E+00 9.23E+09- ,
~
sh+00 ?1.61E+10 l RB-86 0.00E+00 2.23E+10 1.10E+101 0.00E+00 -0.00E+00 <- yo 00 5.70E+08: SR-89. 1.26E+10 -0.00E+00z 3.61E+08 0.00E+00:;0.00E+00- R 4.+00 2.59E+08: -
)
SR-90: J 1.22E+11-~0.00E+00: 3.10E+10, 0.00E+00.'O.00E+00: 0.uu2+00 l'.52E+09: Y-91' 7.33E+04l:0;00E+00 1.95E+03 0.00E+00 0.00E+00 0.00E+00 5.25E+06' ZR-95 6.80E+03 zl.66EF03- 1.18E+03~ 0.00E+00 -1.79E+03- 0.00E+00: 8;26E+05 NB-95 RU-103 5.93E+05 2.44E+05 1.41E+05- 0.00E+00: 1.75E+05 '0.00E+00 2.06E+08 8.67E+03 0.00E+00 2.90E+03; 0.00E+00 1.80E+04L1 0.00E+00 11.05E+05-RU-106 AG-110M 1.90E+05 u 0.00E+00 2.38E+04~ 0.00E+00:'2.25E+05 0.00E+00c l.45E+06 3.'6E+08 2.82E+08 11.86E+08 0.00E+00 4.03E+08 0.00E+00;}1.46E+10'
]
TE-125M 1.51E+08. 5.04E+07 .2.04E+07 5.07E+07 0.00E+00 0.00E+00 7.18E+07 ! TE-127M 4.21E+08 1.40E+08' 5.10E+07. 1.22E+08 1.04E+09 0.00E+001 1.70E+08 0" TE-129M 5.57E+08 1.91E+08 8;58E+07 .2.14E+08~ 1.39E+09-.0.00E+00 .3.33E+08
- i. I-131 2.72E+09, 3.21E+09 -1.41E+09 1.05E+12 3.74E+09 0.00E+00 1.14E+08 I-133 3.63E+07' 5.28E&O7 '1.55E+07 9.61E+09' 6.21E+07' O.00E+00 8.94E+06 <
-I-135 CS-134 '1.12E+05 '2.24E+05 8.'15E+04 2'00Es07 2'49E+05 0.00E+00 28.09E+04 CS-136 3.65E+10' 6.80E+10' 6.87E+09 0.00E+00 '1.75E+101'7'.18E+09 1.85E+08 CS-137 1.9BE+09 5.81E+09 2.17E+09 0.00E+00 '2.32E+09 4'.74E+08 8.83E+07 BA-140 5.15E+10 .6.02E+10 4.27E+091 0.00E+00 1.62E+10 6.55E+09.l1;88E+08 ,
2.41S+08 2.41E+05~ 1.24E+07 0.00E+00 5.72E+04 '1.48E+05 '5.92E+07 I CE-141 4.34E+04 2.64E+04 - 3.11E+03 0.00E+00, 8.16E403 0.00E+00x1.37E+07 CE-144
.PR-143 2.33E+06 9.52E+05 1.30E+05 .0.00E+00' 3.85E+05 0.00E+00' 1.33E+08-I -
ND-147 1.49E+03 :5.55E+02 7.36E+01 0.00E+00 2.06E+02 ': 0.00E+00 7.84E+05, 4 18.81E+02 9.05E+02 .5.55E+01~ -0.00E+00 .3.49E+02 l0.00E400 5.74E+05 j
.i g 'per Units are m'(mrenVyr) Tr uC1/sec, except for tritium,11n mrenVyr uCi/sec. j m
Table 3-5.;Dosa i : tors for Particulates and Iodines lL 'l o 3-39 Gen. Rev. 7 L e t 5 j ' ' ' i s l e'. . (, , , , , . (~ , - * , 1-
~~~
. -. ;. . l W.a t
- W
;. .; e
.a
- a. -0
._y -,
3 i , FNP-0-M-011 1
. Gaseous Effluents 1
[ . L ' Pathway: GOAT MILK' Age Group: ADULTJ ' D Nuclide Bone Liver- T. Body- Thyroid Kidney- ' Lung' GI-LLI- F
.H-3 0.00E+00 ~ l'.56E+03. 1.56E+03 -1.56E+03- 1.56E+03 .1.56E+03 1.56E+03-C-14 2.63E+08 ~5.27E+07. 5.27E+07- 5.27E+07, 5.27E+07. 5.27E+07= 5.27E+07 j
l P-32 _ 2.05E+10! 1.28E+09 ~7.93E+08 ~0.00E+00 0.00E+00 0.00E+00 2.31E+09- _. CR-51 0.00E+00L 0.00E+00 3.43E+03= 2.05E+03 '7.55E+02. 4.55E+03 8.62E+0J. MN-54 0.00E+00 1.01E+06 1.93E+05 0'.00E+00 3.00E+05 0.00E+00~ 3.09E+06 .
~
FE-55 3.26E+05. 2.2'6E+05 5.26E+04-'O.00E+00 0.00E+00E 1.26E+05 1.29E+05 - FE-59 3.86E+05o9.08E+05' 3.48E+05 -0.00E+00 0.00E+00- 2.54E+05= 3.03E+06< l co-58 0.00E+00 5.66E+05 1.27E+06=;0.00E+00 0.00E+00. 0.00E+00:-1.15E+07 Co-60 0.00E+00 1.97E+064 4.34E+06 =0.00E+00 0.00E+00 0.00E+0C .3.70E+07. NI-63 8.07E+08- 5.60E+07 2.71E+0L 0.00E+00. 0.00E+00 .0.00E+00 ~ 1.17E+07 i ZN-65 . 1.65E+08'~5.24E+08 -2.37E+08 J0;00E+00-'3.50E+08 0.00E+00 .3.30E+08. RB-86 'O.00E+00 3.11E+08 1.45E+08 .0.00E+00. 0.00E+00 10.00E+00 6.1'4E+07 c CR-89' '3.05E+09 0.00E+00 :8.75E+07 0.00E+00- 0.00E+00= 0.00E+00- 4;89E+08 i
'SR-90 9.83E+10 0.00E+00 2.41E+10~ 0.00E+00 0.00E+00 0.00E+00 2.84E+09 :i Y-91 '1.03E+03 0.00E+00 2.76E+01" 0.00E+00 0.00E+00' O.00!+00' 5.67E+05 j ZR-95 1.13E+02 3.63E+01. 2.46E+01 .0.00E+00 5.70E+01 0.00E+00 1.15E+05' !
NB-95 9.91E+03 5.51E+03 2.96E+03 0.00E+00 5.45E+03 0.00E+00 :3,34E+07 RU-103 1.22E+02 0.00E+00 5.26E+01 0.00E+00 4.66E+02 .0.00E+00 1.43E+04 RU-106: 2.45E+03 .0.00E+00:.3.10E+02 0.00E+00 4.73E+03 0 00E+00 1 58E+05 .
-AG-110M 6.99E+06 o.46E+06 3.84E+06. 0.00E+00 1.27E+07J 0.00E+00 '2.64E+09 i TE-125M 1.95E+06 7.08E+05 .2.62E+05 ~5.88E+05 '7.95E+06. 0.00E+00 .7.81E+06 3 TE-127M 5.49E+06 1.96E+06 6.69E+05 cl.'40E+06 2.23E+07 0.00E+00 1.84E+07
~
3.64E+07J I-131 TE-129M I-133
.7.22E+06 3.55E+08 5.' 08E+08 2.70E+061.14E+06-2.'91E+08--l.67E+11; 8.71E+08 0.00E+C0 2.48E+06 3.02E+0 j l}
4.65E+06~ 8.08E+06' 2.'46E+06 1.19E+09 -1.41E+07 0.00E+001 ~7.26E+06: - I-135 '1.54E+04- 4.04E+04 1.49E+04l 2.66E+06 6.48E+04 0.00E+00~ 4.56E+04 CS-134 1.70E+10 4.04E+10 3 30E+10 0.00E+00 1.31E+10-?4.34E+09: 7'06E+08 . CS-136 7.90E+08 3.12E+09 ;2.24E+09 0.00E+00 1.74E+09f 2.38E+08 ?3.54E+08' + CS-137 2.21E+10t 3.03E+10- 1.98E+10 n0.00E+00' 1.03E+10'*3~42E+09F~5~.86E+08 BA-140 3.23E+06 4.05E+03- 2.11E+051 0.00E+00 1.38E+03'12;32E+03 .6.64E+06 1 CE-141 5.81E+02 3.93E+02 4.46E+01: 10.00E+00. 1.83E+02;;0.00E+00 1.50E+061 ,. CE-144 -4.29E+04 1.79E+04 2.30E+03 'O.00E+00. 1.06E+04' 0.00E+00 1;45E+07 i PR-143 1.90E+01 7.60E+00 9.39E-01 0.00E+00 4.39E+00;l0.00E+00 8130E+04 ' ND-147- 1.13E+01. 1.31E+01 -7.81E-01! 0.00E+00 7.64B+00 0.00E+00' 6.27E+04 t b 1 Units are m'(mrenVyr) per uCi/sec, except for tritium, in mrrm/yrl per uCi/sec. c Table 3-5. Dose rectors-for Particulates and' Iodines I l 3-40 Gen. Rev. 7 ' [. e l 1 , , 1 M. - i 9 A
- , t d
, .. , .-. , _ ,-_ + - , - - - . - . - - --- ""
q - - - - s
$W ,3.- ,
4 E'.~ FNP-0-M-011 u Gaseous Effluents jPathway: . OCAT MILK j Age Group: TEEN 1
.Nuclide' Bone' Liver T. Body Thyroid ; Kidney Lung GI-LLI H-3 0.00E+00 2.03E+032.03EAn3 '2.03E+03; 2 N3E+03 !2.0'3E+03i 2$03E+03' C 4.86E+08 9.72E+07 9.72Ltu
- P .72E+07 9.72c+07= 9.72E+07 9.72E+07= :i CR-51 3.79E+10 2.'35E+09 1.47E+09 0.00E+00~ 0.00E+00 0.00E+00 3.18E+09 et
'O.00E+00 0.00E+00 5.99E+03 13.33E+03- 1 31E,G3. 8.55E+03-:1'.01E+06- 1 MN-54 10.00E+004 1.68E+06 3.34E+05 !0.00E+00 5.02E+05' 0.00E+00 '3.45E+06- 1
.FE-55 5.79E+05- 4.11E+05' 9.57E+04, 0.00E+00 0.00E+00 2.60E+05. 1.78E+05-FE-59 6.74E+05< 1.57E+06 6.07E+05:'0.00E+00 00.00E+00. 4.96E+05 3.72E+06 CO-58. 0.00E+00 9.$3+0b -0.00E+00 0.00E+00l0.00E+00'.1.31E+07 Co-60 0.00E+00 - 3. A E,7.52E+06
&O6 ' . 0.00E+00:
2.19E+06 0.00E+00 .0.00E+00~,4.35E+07: ji NI-63' 1.42E+09' 1.00S408 4.81E+07l 0.00E+001 0.00E+00 '0.00E+00 1'.59E+07 ,
'ZN-65 RB-86 '2.53E+08 8.78E+08 :4.10E+08 0.00E+00L 5.62E+08 OLO0E+00- 3.72E+08I .1 SR-89 0.00E+00 5.67E+08 1.67E+08~ 0.00E+00='O.00E+00. 0.00E+00 ~8.40E+07' s 5.62E+09 0.00E+00 1.61E+08' O.00E+00 0.00E+00- 0,00E+00;~6.69E+08; 1 SR Y-91. 1539E+11. 0.00E+UOl 3.43E+10: 'O.00E+001 0.00E+00 0.00E+00. 3.90E+09' j
-1.90E+03 0.00E+00i 5.08E+01 0.00E+00 0.00E+00 0.00E+00 7.77E+05' '
ZR-95 NB-95 -1.98E+02 6.25E+01 4 ~. 30E+01- 0.00E+00 9.18E+01 0~00E+00 1.44E+05 . RU-103 1.69E+04 .9.37E+03 5.16E+03 0.00E+00 '9.08E+03' 0.00E+00 14'01E+07 RU-106 2.17E+02 0.00E+00. 9.29E+01 0.00E+00J7.66E+02. 0.00E+00i 1.82E+04- z
-4.50E+03 0.00E+00 5.67E+02 0.00E+00V 8.68E+03 - 0.'00E+00 2.16E+05 .
AG-110M 1.16E+07 1.09E+076.65E+06 0.00E+00 '2.08E+07- 0.00E+00- 3.07E+09
. 4 TE-125M 3'60E+06 1.30E+06 4.82E+05 1.01E+06 :0.00E+00' 0.00E+00L<1.06E+07 -
TE-127M 1.01E+07 3.59E+06 1.20E+062.41E+06- 4.10E+07. 0.00E+00E 2.52E+07:- ' M TE-129M I-131 1.32E+07 4.90E+06 2.09E+06 4.26M065.53E+07?0.00E+00 4 96E407i I-133 6.45E+08 9.03E+08 4.85E+08 '2.63E+11 -1.55E+09 ;0.00E#30 ~ 1.79E+08 8.49E+06 1. 44E+ 07 4.39E+06 2.01E+09 2.52E+07;:0.00E+00 11.09E+07: ; 1 I-135 ! CS-134- 2.74E+04 7.05E+04 2.61E+04 4.54E+06 fl.11E+05 'O.00E+00 -7.82E+04' 2.94E+10 6.93E+10 3.22E+10 0.00E+00 2.20E+10; 8.41E+09= 8.62E+08 i CS-136 1.34E+09 5.29E+09 3.55E+09 0.00E+00: 2;88E+09L 4.54E+08 4.26E+08 4 I CS-137 BA-140 4.02E+10 '5.34E+10 1.86E+10 0.00E+00H1.82E+10?.~7.06E+0917.60E+ 5.82E+06 7.14E+03 3.75E+05 0.00E+00 2.42E+03t 4.80E+03. 8.98E+06? - CE-141 1.07E+03 7.12E+02 8.'18E+01 0.00E+00 '3.35E+023 :0.00E+00 12.04E+06 CE-144 7.90E+04' 3.27E+04 4.24E+03 '. 0.00E+001 l'.95E+04 - : 0.00E+00 1.99E+07-PR-143 3.48E+01 .1.39E+01 1.73E+00: 0.00E+00 8.08E+00.~0.00E+00x ;1.15E+05
. ND-147 2.17E+01 2.36E+01' 1.42E+00 0.00E+00 ; 1.39E+01~ 0.00E+00 8.53E+04 6 i Units are m'(mrenVyr) per uCi/sec, except for tritium,' .in mrenVyr per uci/sec. ]
Table 3-5. Dose Factors for Particulates'and Iodines 1 3-41 Gen. Rev.'7. g i L
' u
- }. ...
7~ 4.y ; - r
'3 ' '"
' j flL kj_ .i _ ,
.c
; ,x ,, - . L A A- -- -- -
3
q 1
. 'FNP-0-M-0111 ~!
Gaseous Effluents Pathway: GOAT MILK Age Group: CHILD Nuclide Bone. Liver T. Body Thyroid Kidney Lung. L. GI-LLI- 0 H-3c C-14 0.00E+00 '3.20E+03. 3.20E+03: 3.20E+03: 3.'20E+03. 3.20E+03 3.20E+03 1.19E+09i 2.39E+08 2,39E+08 2.39E+08 2.39E+08. 2.39t+08 2.39E+08. P-32. i CR 9.34E+10 4.37E+09 3.60E+09 0.00E+00 0.00E+00 0.00E+00 E2.58E+09 i MN-54 0.00E+00. 0.00E+00 1.22E+041 6.78E+03 1.85E+03::1.24E+04: 6. 48E+05 0.00E+00' 2.52E+06 6.70E+05' O.00E+00 7.06E+05 0.00E+00 2.11E+06 rE-55 rE-59 1.45E+06'17.71E+05J 2.39E+05 .0.00E+00: 0.00E+00N4.36E+05 :1.43E+05 ,
- Cow 58 1.56E+06 2.53E+0611.26E+06 0.00E+00' O.00E+00' 7'33E+05- 2'63E+06~ Er i
-Co-60 -0.00E+00 1.45E+06 4.45E+06 .0.00E+00 .0.00E+00' O.00E:.00-l8.49E+06 0.00E+00.15.18E+06~ 1.53E+07J 0.00E+00 7 0.00E+00.:0,00E+001;2.87E+07 NI-63 3.56E+09: 1.90E+08 11.21E+08 0.00E+00' 0;00E+00 0.00E+00. 1.28E+07. _
-ZN-65: 4.96E+08, 1.32E+09 8;22E+08 0' 00E+00 ~ 8;33E+08 .0.00E+0012.32E+08 -
RB-86 : SR-89 0.00E+00 1.05E+09~ 6.47E+08 '0.00E+00 0.00E+00- 0.00E+00 6.77E+07 ; SR-90 1.39E+10 0.00E+00 '3.97E+08' O.00E+00 0.00E+00 0.00E+00? 5.38E+08- ! Y-91 2.35E+11 =0.00E+00 15.95E+10 0.00E+00- 0.00E+00' O.00E+00' 3.16E+09- !! 4.68E+03 'O.00E+00 .1.25E+02' O 00E+00 0.00E+00 .0.00E+001 6.24E+05 I ZR-95 NB-95 4.60E+02 ,1.49E+04 3.81E+04 1.01E+02 -.1.06E+04 9.00E+01. ~ 0.00E+00 ' 1.45E+02i 0.00E+00. 1.05E+05: ) 0.00E+00. 1.40E+04 =0.00E+00= 2.7CE+07, ' RU-103 5.14E+02 0.00E+00' 1.98E+02 0.00E+00 1.29E+03' O.00E+00;11.33Ev04: RU-106 1.11E+04 0.00E+00 38E+03:.O,00E+00- 1,50E+04 0.00E+00- 1.72E605 , AG-110M 2.51E+07 1.69E+07. 1.35E+07 0.00E+00 3.15E+07. '0.00E+0012.01E+09 TF-125M 8.85E+06 .2.40E+06' 1.18E+06 2.48E+06. 0.00E+00 0.00E+00 '8.54E+06
+ TE-127M 2.50E+07 6.72E+06 2.96E+06 5.97E+06. 7.12E+07; 0:00E+00'.2.02E+07- "
LTE-129M I-131 3.26E+07 <9.09E+06 '5.06E+06 1.05E+07 9.56E+07E 0.00E+00~ 3.97E+07 f 1.56E+09 1.57E+09 8.94E+08 5. 20E+111 : 2;58E+09J0.00E+00 l'. 4 0E+08 - I-133, 1 2.06E+07. 2.55E+07 9.65E+06 .4.74E+09 4.25E+07' O.00E+00- 1.03E+07 l t 1-135 L CS-134 6.49E+04 1.17E+05 5.52E+04 1.03E+07f1.79E405?0.00E+00 8.90E+04' L CS-136- 6.79E+10 1.11E+11 2.35E+10 0.00E+00~L3.45E+10 1.24E+10 6-01E+08! l 3.04E+09 .8.34E+09 5.40E+09 10.00E+00."4;44E+09? 6.63E+08 12.93E+08 CS-137 BA-140 9.67E+10 9.26E+10 l.37E+10. : 0.00E+00 3.02E410: 21.09E+10. 5.'80E+081 1.41E+07 1.23E+04. 8.20E+05 0.00E+00: 4.01E+03 37.34E+03 17.12E+06 CE-141 1 ' CE-144 2.63E+03 1.31E+03 1.94E+02 0.00E+00 5.74E+02' O 00E+00 .1.63E+06 1.95E+05 6;11E+04 1.04E+04 0.00E+00 3.38E+04 0.00E+00 11.59E+07' PR-143 ND-147 8.62E+01 - 2.59E+01L 4.28E+00 0.00::+00' 1.40E+01w 0' 00E+00 19.30E+04 : 5.34E+01 4.32E+01 3.35E+00 t0.00E+00 2.37E+011 0.00E+00: 6.85E+04 ! 2 Units per1uci/sec. are m (mres/yr) per uC1/sec, except for tritium,-in mrem /yr ' 4 Table 3-5 Dose Factors for Particulates and Iodines' b 3-42 fGen.LRev. 7: 1 j i + G
'a .
,- A a 91 l .
. = = = - _- . - .. ~-- ..
i n i ,
)
MP-0-M-011 i Gaseous" Effluents' l Iathway GOAT MILK. Age group: INFAlff Nuclidet Bone . Liver T. Body 'Ihyroid . Kidneyi Lung' 'GI-LLI
~
~H-3 0.00E+00. 4;86E+03: 4.86E4 03 : 4.86E+03 4.86E+03 4.86E+03 14.86E+03
'C-14 2.34E+09: 5.00E+08 5.00E+08 5.00E+08 5.00E+08 5.00E+08>15 A0E+08-
'P-32 1.92E+11- 1.13E+101 7.46E+09 ,0.00E+00- 0.00E+00 0.00E+00 2.60E+09 CR -0.00E+00 0.00E+00 '1.94E+04' 1.26E+04' 2,76E+03 K2.46E+04 5.64E+05-' J MN-54 0.00E+00: 4.48E+06 1.06E+06L 0.00E+00 :1.04E+06 0.00E+00- 1.72E+06' FE-55 '1~.76E+06 11.13E+061 3.03E+05' 0.00E+00L 0.00E+00 ' 5S55E+05 c 1.4NEN05;.
FE-59 co-58' 2.92E+06< 5.10E+06~ 2.01E+06 0.00E+00 0.00E+00?'1.51E+06 '2.43E+06-
.Co-60 O.00E+00 '2.91E+06 7.26E+06' 0.00E+00ll0.00E+00 0.00E+00: 7.25E+06: i
'O.00E+00: 1.06E+07 2.50E+07 0.00E+00V 0.00E+00f.0.00E+00i-2.52E+07 J NI-63 4.19E+09 2.59E+08 1.45E+08' 0.00E+00 0.00E+00. 0.00E+00:-1.29E+07- q ZN .
,h RB-86 6.66EA08=2.28E+09 1.05E+09 0.00E+00 '1.11E+09' 0.00E+00 E1.93E+09 -.
0.00E+00' 2.67E+09. 1.32E+09-'O.00E+00 ;0.00E+00 0.00E+00. 6.83E+07:
'SR-89 2.64E+10 0.00E+00':7258E+08 :0.00E+001 0.00E+00 0.00E+00-;5.43E+08'
.SR-90 1 Y-91. 2.55E+11 0.00E+00 6.50E+10 0.00E+00 ~0'.00E+00 = : 0.00E+00 13:19E+09i 8.79E+03. 0.00E+00 2.34E+02L 0.00E+00 0.00E+003 'O.00E+00y6.30E+05- q ZR-95 NB-95 8.17E+02 -1.99E+02 -1.41E402 0.00E+00 12.14E+02? 0.00E+00- 9.91E+04
- RU-103 7.12E+04- 2.93E+04 1.70E+04 ~0.00E+00: 2.10E+04 0.00E+00 2.48E+07.
RU-106 1.04E+03 0.00E+ 00 3.48E+02. 0.00E+00 .2.17E+03 0.00E+00 l'.27E+04. 2.28E+04 0.00E+00 2;85E+03. 0.'00E+00 >2.70E+04UO.00E+00 :1.73E+05; AGA110M 4.63E+07 :3.38E+07: 2.24E+07 0.00E+00 .4.83E+07 .0.00E+00: 11.75E+09' , TE-125M 1.81E+07 6.05E+06 2.45E+06< 6.09E+06L 0.00E400 0.00E+00 J8.62E+06 1 TE-127M 5.05E+07 1.68E+07 6.12E+06 ' 1.46E+07 1.24E+08J 0.00E+00 12.04E+07: ! TE-129M. 6.69E+07. 2;29E+07 .1.03E+07: 2.57E+07 -1'.67E+08L'O.00E+00: 3.99E+07/ ' I-131 3.26E+09' 3.85E+09' 1.69E+09 ~ 1.26E+12 c4.49E+09 :0,00E+00 1.37E+08. I-133 ( 4.35E+07 6.34E+07 1~.86E+07 : '1' 15E+10 7'.45E+07 0.00E+00 1.07E+07 ' I-135' 1.35E+05 2.66E+05 9'79E+04 2.41E+07 2.99E+05 50;00E+00 9.71E+04 CS-134 CS-136 1.09E+11 2.04E+11 2.06E+10 0.00E+00: 5.25E+10 2.15E+10 '5.54E+08- - d L 5.93E+09 1.74E+10 6.51E+09 :0.00E+00 .6.95E+09 fl.42E+09J 2'.65E+08 i l~ CS-137' BA-140 1.54E+11" 1.81E+11 1.28E+101 0.00E+00 4.85E+10< 1.96E+10' 5.65E+08 i 2.89E+07 '2.89E+04 1 A9E+06 .0.00E+0C 6.87E+03'11.78E+04' 7.10E+06- .J CE-141 5;20E+03 3.17E+03~ 3.74E+02 0.00E+00 3.79E+02?i0'.00E+00 "1.64E+06
- CE-144:
PR-143 2.79E+05 1.14E+05- 1.56E+04 0.00E+00-'4.62E+04i 0.00E+00 1.60E+07' 1.78E+02 6.67E+010 8.84E+00D 0.00E+00 2;48E+01E 0.00E+00: 9.41E+04' l ND-147-1.06E+021 1.09E+02 6.66E+00 :0.00E+00 4.19E+01. 0.00E+00.t6.88E+04 s
-per Units;are uCi/sec.
m* (mrenVyr) per uti/sec, except for tritium, . in mrem /yr
~
3 Table 3-52 Desa Factors for Particulates and Iodines: g 3-43' Gen.'Rev. 7 1 l q 4 j
@ , Ot l $ fl4 a p" .
i, ,
,/
- FNP-0-ti-011 i
, -Gaseous' Effluents' '
- Pathway: MEAT ~ A9e Groups ADULT- ]
Nuclide Bone Liver T. Body . Thyroid. Kidney ' Lung. GI-LLI H C 0.0cr+00 :3.25E+02 3.25E+02 3.25E+02 3.25E+02 ' 3.25E+02 : 3.25E+02 - i P-32 2.41E+08J'4.83E+07 4.83E+07T ' 4.83E+07: 4.83E+0 / 4.83E+07 c4.83E+07
- 4.66E+09' 2.90E+08 ;1.80E+08 -0.00E+00; 0.00E+00 -0.00E+00 .5.24E+08- !
CR-51 MN 0.00E+00.. 0.00E+00 .7.05P:+03 4.21E+03. 1.55E+03 9.35E+03 1.77FiO6-0.00E+00' 9.18E+06 1.75E+06 0.00E+00- 2.73E+06 0.00E+00 l2.81E.47 _ FE-55 ' FE 2.93E+08- 2.03E+08.- J4.72E+07I 0.00E+00 0.00E+00 1.13E+08L li16E+08: 2.66E+08E 6.24E+08 2.39E+08 0.00E+00 0.00E+00 !<.74E+08;-2.08E+09! , co-58 co 0.00E+00 1.82E+07 74.09E+07 0.00E+00 0.00E+00~ 0.00E+00 i3.69E+08- m 0.00E+00 17.52E+07. z 1.66E+08 ' -0.00E+00 0,00E+00 0.00E+00 i:1.41E+09; 1 NI-63 1.89E+10.'1.31E+09L ^.33E+08i.0.00E+00:'0.00E+000;00E+00 :2.73E+08' ZN RB-86 '3.56E+08 1.13E+091 5.12E+08' O.00E+00 7.57E+08~ 0.00E+0'0 t 7.13E+08 SR-89 0.00E+00 4.87E+08= 2.27E+08 0.00E+00 0.00E+00- 0.00E+00 9.61E+07 q
'SR-90 3.02E+08 0.00E+00=:8.66E+06 0.00Ev00 0.00E+001 0.00E+00- 4.84E+07L , p 1.24E+10D0.00E+00 3.05E+09 .0;00E+00- 0.00E+00 L0.00E+00 3.59E+08: '
Y '1.13E+06 0.00E+00 3.03E+04 0.00E+00 0.00E+00* 0.00E+00 % 23E+08 ' ZR-95 1.87E+06 6.01E+05 4;07E+05--0.00E+00 9.43E+05 0.00E+00 1.90E+09. , NB-95' 2.30E+06 1.28E+06; 6.87E+05 'O 00E+00- 1.26E+06 0.00E+00 7.76E+J9 RU-103 i
- RU-106 1.05E+08 0.00E+00 4.53E+070.00E+00-:4.02E+08 0.00E+00E1.23E+10 ,
2,80E+09. 0.00E+00 3.54E+08 0.00ra00 5.40E+091 0.OCE+00f 1.81E+11 .i AG-110M~=6.68E+06 6.18E+06: 3.67E+06- 0.00E+00: 1.22E+07 0.00E+00ti2.52E+09- }
-TE-125M 3.59E+08 l'.30E+08 14'81E+07c 1.08E+C8 '. 46E+09 70.00E+00 1.43E+09 N
TE-127M1.13E+09 TE-129M 1.12E+09 3.99E+08 L1-.36E+08 2.85E4 08 : 4.53E+09 0.00E+00 '3.74E+09: 4 4.23E+08--1.80E+08. 3.90E+08' 4.~73E+09 0.00E+00, 5.71E+09
-I-131 1.07E+07 1.54E+07~ 8.81E+06 5.04E+09; 2.63E+07 0.00E+00' 4.05E+06 I-133 -
4 3.67E-01 6.38E-01 1.94E-01 9.37E+01E.1.11E+00 0.00E+00.15.73E-01 , I-135 n . 1 l CS-134 .:.47E-17 .1.17E-16 4.32E- 17' 17.73E-15 L1.88E 0.00E+00 .1.32E-16 l
- CS-136 6.58E+0R 1.56E+09 1.28E+09- 0100E+00!'5.06E+08
- 1.6SE+08' 2.74E+07 '
1.21E+07 4.76E+07 3;43E+07Q 0.00E+00 2.65E+07' 3.63E+06- 5.41E+06 CS-137 BA-140 8.72E+0B 1.19E+09. 7.81E+081 0.00E+00 4.05E+08. 1.35E+08. 2.31E+07; 4 l 2.87E+07 3.61E+04' l'.88E+06 0.00E+00* 1.23E+04 ,2.07E+04 -5.92E+07- j . CE-141 - 1.40E+04 9. 50E+03 : ' 1. 08E+03 0.00E+00 4.41E+03 i CE-144-1.46E+06 6.09E+05 17.83E+04 0.00E+00 3.61E+05; 0.00E+00- 14 93E+08 O'.00E+00' 3.63E+07 l PR-143 2.'10E+04 8.41E+03- 1.04E+03 40.00E+00: 4.86E+03;:0.00E+00 9.19E+07 1
'( I ND -147 7.07E+03 8.17E+03 4.89E+02 0.00E+00 '4 78E+03 0.00E+00" 3.92E+07 j,
Units are m'(mrenVyr) per uCi/sec, except for. tritium, in mronVyr ~ per uC1/sec.- ' 1
- Table 3-5., Dose. Factors for Particulates and Iodines 1
3-44 Gen. Rev. 7 4 i .
]
+i 1 3 y
a3 .-- l.- m .,
^ FNP-0-M-011
' Gaseous' Effluents'
'Y Pathway: MEAT Age Group: TEEN Nuclide -Bone Liver. T. Body Thyroid? . Kidney : Lung .GI-LLI H 0.00E+00 1.94E+02 1.94E+02 1.94E+02L d.94E+02 l'.94E+02 1.94E+02' C-14 2.04E+08L 4.08E+07. 4.08E+07 '.4.08E+07 1.08E+07 - 4.08E+07; 4.08E+07 P-32 3.94E+09 2.44E+08 1.53E+08. 0.00E+00-~ 0.00E+00 0.00E+00 3.31E+08 CR-51 ]
'O.00E+00 0.00E+00. 5.64E+03 3.13?+03 1.24E+03"8 05E+03 9.47E+05 .
MN-54 0.00E+00 -7.00E+06 1.39E+06 0.00F 00 2.09E+06 0.00E+00 ,1.44E+07.
-FE-55 2.38E+08; 1.69E+08 '3.94E+07. 0.00E+00 0.00E+00i11.07E+08V7i31E+07 FE-59 2.12E+08> 4.95E+08 1.91E+08 'O.00E+00-'0.00E+00; 1.56E+08M 1.17E+09-CO-58; 0.00E+00 -1.41E+07 -3.24E+07 0.00E+00: 0.00E+00 ' 0.00E+00 1.94E+08 ,
co-60i 0.00E+00. 5.83E+07 1.31E+08 0.00E+00' O.00E+00 l0.00E+00, 7.60E+08 NI ;
-1.52E+10 1.07E+09 5.15E+08 .0.00E+00 *0.00E+00 0.00E+00-~1.71E+08: ,
. ZN -65 RB-86 2.50E+08 8.69E+08' 4.05E+08 :0.00E+00 5.56E+08 .0.00E+00~.3.68E+08 0.00E+00' 4.07E+08' 1.91E+08' O.00E+00 0.00E+00, 0.00E+00, 6.02E+07
- SR-89 2.55E+08' O.00E+00t 7.29E+06 -0.00E+00=;0.00E+00L 0200E+00 3.03E+07.
-SR-90 Y 8.05E+09 0.00E+t'0 l'.99E+09 - ' O.00E+00 < 0.00E+00 0.00E+00 2.26E+08' 0.54E+05 0.00E+00 2.56E+04 0.00E+00A0.00E+00 0.00E400- 3.91E+08' 3 ZR-95 1.50E+06 4.73E+05 3.25E+05; 0.00E+00 '6;95E+05 10.00E+00: 1.09E+09.
'NB-95 RU-103 .1.79E+06 9.95E+05 '5.48E+05. 0.00E+00 .9.65E+05 LO.00E+00- 4.26E+09 8.57E+07;'O.00E+00 3.66E+07 - 0.00E+00 ' 3.02E+08 0.00E+00D 7;16E+09 :
RU-106 2.36E+09'.0.00E+00 2.97E+08 : 0.00E+00 4.53E+09 0.00E+00- 1.13E+11 AG-110M 5.06E+06 4.79E+06' 2.91E+06 0.00E+00 19.13E+06 -0.00E+00 -1,34E+09 - TE-125M 3.03E+08 1.09E+08 '4.05E+01.-8.475+07 0.00E+00 0200E+00 8.94E+08 TE-127M 9.41E+08 3.34E+08 1.12E+08 '2.24E+08 :3'.82E+09 0.00E+00- 2.35E+09; l TE-129M I-131 9.50E+08 3.53E+08 1.50E+08 3.07E+08 3.97E+09. 0.00E+00 3.57E+09 8.93E+06 1.25E+07- 6.71E+06' 3.65E+09 2.15E+07; 0.00E+00 :2.47E+06 7 I-133 3.07E-01' 5.20E-01 1~.59E-01 7.268+01 19.12E-01 'O.00E+00 3.93E-01 I-135-CS-134 3.64E-17 9.37E-17 3.47E-17. - 6.03E-15 .1.'48E-16 : . 0.00E+00 - -1.04E-16 5.23E+08- 1.23E+09 5.71E+08 0;00E+001i3.91E+08L 1.49E+08. 1.53E+07-CS-136 CS-137 9.40E+06 3.70E+07 1 2.48E+07 0.00E+00 :2.01E+07? :3.17E+06 : 2.98E+06 di 7.24E+08' 9.63E+08 '3.36E+08 0.00E+00 3.28E+08 1.27E+08, 1.37E+07 BA-140 2.38Ew7 2.91E+04 1.53E+06 ' O.00E+00 9.87E+03 1.96E+04 ;3.66E+07 CE-141 1.18E+04 7.88E+03 9.05E+02 .0;002+00 .-3.'71E+03 0.00E+00, 2.25E+07 - CE-144 1.23E+06 5.08E+05 '6.60E+04! 0.00E+00 03;04E+051 0.00E400 3.09E+08.
-PR-143
'ND-147 l'.76E+04 7.04E+03 8.78E+02: 0.00E+00 4.09EA03 0'00E+00 5'.81E+07 .
6.23P:+03 - 6.78E+03 4.06E+02 0.00E+005 -3.98E+03: 0.00E+00' 2.44E+07 _ Units are m* (mrenVy.) per uci/sec, except for tritium,: in mrem /yr - per uci/sec. Table 3-5. Dose Factors for Particulates and Iodines E45 Gen. Rev. 7 e y.
q- ..
- r. 3 FNP-0-M-011 l
[ '. Gaseous' Effluents. q
?athway: MEAT '
iroup: CHILD"- i
.Nuclide' Bone' -
T. Body' Thyroid Kidney Lung GI-LLI i
~H-3 C 0'.00E+00 2.34E+02-:2.34E+02 2.34E+02 2.34E+02 2.34E+021 '2.34E+02' l 3.83E+08 7.67E+07 7.67E+07' 7.67E+07 7.67E+07 7.67E+07' 7.67E+07' P-32 7.43E+09 3.48E+08. 2.86E+08 .0.00E+00 0.00E+00 0.00E+00 2.05E+08 CR-51T 0.00E+00 0.00E+00 8.79E+03 l4.'88E+03l 1.33E+03 8.91E+03 4.66E+05L hu-54< -0.00E+00 8.01E+06- 2.13E+061 0.00E+00' 2.25E+06 0.00E+00" 6.72E+06- >
~
FE-55 4.57E+08: '2;42E+08' 7.51E+07 C.00E+00 -0.00E+00 1.37E+08 4.49E+07-rE-59 3.76E+08 '6.09E+08 3.03E+08- 0.00E+00 0.00E+00 1'.77E+08.-6.34E+08 - CO-58 0.00E+00 1.64E+07 5.03E+07.'0.00E+00 0.00E+00: 0.00E+00 .9.58E+07l co-60. 0.00E+00 6.93E+07 :2.04E+08 0.00E+00 - 0.00E+00 0.00E+00L;3.84E+08: i; NI-63 2.91E+10 11.56E+09 9.91E+081 0.00E+00; 0.00E+00. 0.00E+00.:1.05E+0Si ; ZN-65 3.75E+08 1.00E+09' 6.22E+08' O.00E+00 6.30E+08~ 0.00E+00 Li.76E+08' t
'RB 0.00E+00 5.77E+08--3.55E+08' O.00E+00: 0.00E+00 0.00E+00 .3.71E+07 l SR-89. 4.82E+08: 0.00C+00 1.38E+v7 0.00E+00i 0.00E+00 0.00E+00 '1.87E+07f i SR-90 'l 04E+10 0.00E+00 2.64E+09 0.00E+00= 0.'00E+00- 0.00E+00J1.40E+08: 'l Y-91 1.80E+06. 0;00E+00 4.82E+04 . 0.00E+00 - 0.00E+00 0.00E+00 2.40E+08' M ZR-95 2.66E+06 5.86E+05 5.21E+05 'O.00E+00 8.38E+05 0.00E+00i 6.11E+08-NS-95 3.10E+06 1.21E+06' 8.62E+05 0.00E+00~'1.13E+06: 0.00E+00" 2.23E+09:
RU-103 1.55E+08'.0.00E+00 -5.96E+07' O.'00E+00:i3.90E+08l 0.00E+00< 4.01E+09 - RU-106 4.44E+09 0.00E+00 :5.54E+08 0.00E+00 15.99E+091 0.00E+00' 6.90E+10 AG-110M-;8.39E+06 5.67E+06 4.53E+06 ;- 0.00E+00 31.06E+07' ; 0.00E+00l 6.74E+08 - TE-125M 5.69E+08 1.54E+08 '7.59E+07 1.60E+08 ' O.00C+00 :0,00E+00: 5'49E+08 TE-127M 1.77E+09 4.78E+08 2.11E+08 4.24E+08= 5.06E+09 0;00E+00 1.44E+09i H TE-129M. 1.79E+09 5.00E+08 .2.78E+08 :5.77E+08L 5.26E+09 LO.00E+00: 2.18E+09) . I--131- 1.66E+07 1.67E+07 9.46E+060 L 5. 51E+0912.73E+07: 0.00E+00 L1.48E+06~ I--133 5.7.0E-01 -7.04E-01 _-2.66E-01 1.31E+02' 1.17E+00' 0;00E+00 2.84E-01 I-135 6.59E-17 1.19E-16 5.61E-17 'l.05E-14 l'.82E-16 ' l 0.00E+00 9.04E !4 CS-134 9.22E+08 1.51EP9 3.19E+08 '.0.00E+0014.69E+081 1.68E+08:'8.16E+06' CS-136 1.62E+07 4.46E+07 ^2.89E+07 -0.00E+00 2.37C+07 3.54E+06 1.57E+06 CS-137 1.33E+09 li28E+09. 1.88E+08. 0.00E+00 4.16E+08E l'.50EF08 7.99E+06 3
,BA-140. '4.39E+07 3.84E+04 .2.56E+06 0.00E+00 li25E+04. 2.29E+04: 2.22E+07 '
3 CE-141 2.22E+04 1.11E+04 1.64E+03 0.00E+00 14.86E+03L20 00E+00S 1'.38E+07 CE-144 2.32E+06 .7.26E+05L l'.24E+05 0.00E+00 '4.02E+05< 0.00E+00.11'.89E+08; PR-143 3.34E+04 1.00E+04; 1.66E+03' 0.00E+00 5.43E403 J0.00E400?'3.60E+07 N ND-147 1.17E+04 9.47E+03 7.33E+02' 0.00E+00 5.20E+03:.O'.00E+005 1;50E+07. '? 2 Units ai.e m (mrenVyr) per uC1/sec, except for tritium, fin mrem /yr - per uC1/sec. ~ i n , . _ 4 Table: 3-5. Dose Factors for Particulates and Iodines , i 3-46 .' Geni Rev. 7- ,
- u
'r / (' .?
s ,
$. ! i l l : b i . [T g
.{t i
$ 4 A 4J h[ . , . . , '
.aCm_.:-,-.' + - i-- -
zf 1 Gaseous Effluents 1 Pathway::; VEGETABLE Age Group ( ADULT / I 'Nuclide Bone Liver T. Body -Thyroid PJdney Lung GI-LLI-
.H-3 I C 0.00E+00 2.26E+03: 2.26E+03 ~2.26E+03~ 2.26E+03 2.26E+03: 2.26E+03 2.28E+08 4.55E+07- 4.55E+07 4.55E+07 ;4.55E+07 4.55M07 4.55E+07 -
- P-32 1.41E+09 8.74E+07 5.44E+07! 0.00E+00 -0;00E+00: 0.00E+00 -1.58E+0B
~
J CR-51 16 -54' 0.00E+00. 0.00F+00 4.64E+04 2.78M04 1.02m 04 6'.16E+04 1.17E+07 '! O.00E+00 3.13 D08 5.97E+07 - 0.00s4 00 ' 9.31E+07 0.00E+00- 9.59E+08- 4 FE-55 TE-59 2.10E+08- 1.45E+08 3.38E+07 0.00E+00 .0.00D 00 0.08E+07 8.31E+07 I co-58 1.26E+08 2.96E+08 - 1.14E4 08 0.00E+00 0.00E+00 "8.2BE+07. 9.88E+08- ; Co-60 0.00E+00. 3.07E+07 6.89E+07 0.00E600 0.00E+00 0.00$00- 6.23E+08:- 0.00E+00 1.67E+08 3.69h08- 0.00E400 0,00E+0010.00h00. 3.14E+09 NI-63
-1.04E+10 7.21E+08 3.49E408 .0.00E+00 0.00c+00: 0.00E+00 -1.50E+08~ '
ZN-65 3.17E+08 ' 1.01E+09 - 4.56E+08 0.00E+00 175E+08 0.00E+00 6.36E+08
'RB-86 SR-89 0.00E+00- 2.19E408 1.02E+08 .0.00E+00 0.0DE+00' O.00E+00 4 =.'3 3E+07 9.97E+09 x0.00E+00 .2.86E+08 0.00D 00 -0.00E+00-'O.00E+00 -1,60E+09 SR-90 6.05E+11- 0.00E+00 .1.48E+11- 0.00E+00 0.00E+00 0.00E+00 al.75E+10 Y-91 5.11E+06 0.00E+00 1.37E+05 -0.00E+00 '0'.00E400'-0.00E+00 2.81E+09 ZR-95 NB-95 1.17E+06 3.77E+05 2.55E+05 0.00E+00' 5.91E+05 ?0.00E+00 1.19E+09 .;
RU-103 1.42E+05 ~7.92E+04 4.26E+04 0.00E+00 7.83E+04 0.00E+00 - 4.81E+0S i RU-106 4.77E+06 0.00E400 2.06E+06 0.00Et00 1.82E+07'10.00E+00 5.57E+08- , 1.93E+08 0.00E+00. 2.'44E+07 0.00E+00 3.72E+08 0.00E+00. 1.'25E+10 AG-110M 1.05E+07 '9.75E+06 5.79E+06 0.00E+00 1.92E+07 0.00E+00;'3.98E+09-TE-125M 9.66E+07 3.50E+07 1.29E+07 2.90F,07 3.93E+081-0!.00E+00 3.86E+08 TE-127M 3.49E+08 1.25E+08 4.26E+07 8.92E+07 1.42E+091 0.00E+00' 1.17E+09~ TE-129M I-131 2.51E+0B ?.38E+07 3.98E+07 8.64E+07 1.05E+09f 0.00E+00 '1.27E+09 1 I-133 8.08E+07 1.16E+08 6.62E+07' 3.79E+10. 1.98E+08 LO.00E+00' 3.05E+07; y 2.09E+06. 3.63E+06 1.11E+06 S.33E+081 6.33E+06~ -0.00E+00 3.26E+06-I-135 3.90E+04 1.02E+05 3.77E+04 ~6.74E+06 - l CS-134 l'. 64E+05 L : 0200E+00: 1.15E+05 4.67E+09 1.11E+10' 9.08E+09 0.00E+00 E3.59E+094 ' 1".19E+09;:1.94E+08 CS-136 CS-137 4.27E+07 1.69E+08 -1.21E+08 0.00E+00 9.38E+07' 1.29E+07: 1.91E+07 BA-140 6.36E+09 8.70E+09 5.70E+09 0.00E+00; 2.95E+09 9'81E+08- 1.68E+08' . 1.29E+08 1.61E+05 8.42E+06 0.00h00; 5;49C+04:(9.24E+04 2.65E+08 -l u - CE-141 CE-144 1.97E+05 '1.33E+05 1.51E+04 0.00E+00L'6.19E+04 0.00E+00' 5.10E+08'
~
PR-143 3.29E+07. 1.38E+07 1.77E+06 0.00E+00: ' 8.16E+05 l0.00Et00 1.11E+10 ND-147 6.26E+04 2.51E+04 3.10E+03 ,0,00E+00' 1.45E+04 0.00E+00 2.'74E+08 o l 3.33E+04 3.85E+04 2.31E+03~ 0.00E+004 2;25E+0C '0.00E+00L l'.85E+08" 2 Units are m (mreuvyr) per uC1/sec, except for tritium,.in arem/yr pet uCi/sec. Table 3-5. Dose Factors for Particulates and Iodines-b 3-47 Gen. Rev. 7 +
- k. l c
f .. e --
,#v-,- y 6 + - . . * ~ 6
+, - ( , y v' ~ '- -- -
=~
-= - ' -- - - -
~y ~
hb (.
. FNP-0-M-011
$." [ s Gerecus Efflu nts
' Pathways VEGETABLE' Age Group:: TEEN q
Nuclide' Bone. .' Liver T. Body? Thyroid Kidney Lung GI-LLI-H-3 0.00E+00 2.59E+03- 2.59E+03: 2.'S9E+0312.59E+03 2.59E+03 2.59E+03 j C-14 ~3.69E+08 7.38E+07 17.38E+07; 7.38E+07 7.38E+07c 7.38E+07 7.38E+07 ' P-32 1.61E+09 ~.?9E+07 6.25E+07- 0 00E+'10 0.00E+00 0,00E+00 '1.35E+08-CR-51 0.00E+00 0.00E+00: 6.17E+04 '3.43E+04 '.'35E+04 8.81E+04 'f.04E+07c MN 54- - 0.00E+004.54E+08 i9.01r*07 0.00E+00: 1.36E+08 0.00E+00 -9.32E+08
.FE-55 3.26E+0S 2.31E+08 '5.39E+07J 0.00E+00' 0.00E+00 1.47E+08511.00E+08 FE-59= ' 1.79E+ 09 4;19E+08 1.62E+08 'O 00E+00-~ ).00E+00L 1.32E+08 :9.90E+0B,
- C-58: 0.00E+00 -4;36E+07' 1.00E+08 .0.00E+00 .00E+00 0.00E+00 6.01E+08 Co-60 0.00E+00 2.49E+08 5.60E+08- 0.00E+00; v.00E+00 0.00E+00' 3.24E+09 NI-63 1.61E+10' 1.13E+09; 5.4SE+08, 0.00E+00 0.00E+00 0.00E+00' 1.81E408L i
-ZN-65 -4.24E+08l'1.47Ev09 6.87E+08 0.00E+00 9.42E+08' 0.00E+00o .6.23E+08 RB-86 r SR 0.00E+00- 2.745+08. I'.29E+08 m0.00E+00 0.00E+00 0.00E+00_l4'.05E+07 1.51E+10::0.00E+004.34E+08 0.00E+00 0'.00E+01 0.00E+00 11.80D09 .
SR-90 z7.51E+11 0.00E+00 .1'85E+11.' O.00E+00. 0.00E+00' O.00E+00 2.11E+10L 1 Y 7.84E+06 0.00E+00 - 2.10E4 051 0.00E+00 - 0.00E+00 0.00E+00 l 3.21E+03-4
'l
,4 ZR-95 NB-95 1.72E+06 5.43E+05 3.74E405 0.00E+00 7.98E+05: 0.00E+00^ 1.2SE+09 9 l
1.92E+05 1.07E+05 .5.87E+04 0.00E+00--1.03E+05 0;00E+00 4.56E+08 - RU-103-6.82E+06 :0.00E+00 '2.92E+061 0.00E+00' 2.41E+07 0.00E+00 5.70E+08-RU-106 3.10E+08 0.00E+00 3.90E+07 .0.'00E+00 5.97E+08 10.005+00J 1.48E+10 ; AG-110M 1.52E+07 1.43E+07. 8.72E+05'10.00E+00. 2.74E+07 1 0.00E+00; 4.03E+09 _ .l TE-125M 1'.48E+08- 5.34E+07 '1.98E+07J 4.14E+07. 0.~00E+00;;0.00E400,'4.38E+08-TE-127M ~5.52E+08 1.96E+08' 6.56E+07 ~1.31E+08( 2.24E+09 0.00E+00. l.37E+09-. q I TE-129M 3.62E+08' 1.34E+08 5.73E+07 1.17E+08 ;1.'51E+09; 0.00E+001 1.36E+091 - 4 I-131 7.69E+07' 1.08E+08 . 5;78E+07i.3.14E+10Ml'.85E+08'i0~00E+00 -.2.13E+07: l .I-133 q 1.94E+06 3.29E+06 1~.00E+06=-4.59E+08 f5'7.7E+06 0100E+00t'2J49E+06 I-135 3.52E+04 9.07E+04 3.36E+04 5.84E+06 Jr.43E+05' 0.00E+00 E1.01E+05
- _ CS-134 L CS -136 7.10E+09' 1.67E+10 7.75E+09~ 0.00E+00 5.31E+09 2.03E+09 -2.08E+08 L
CS-137 4.38E+07 1.72E+08 1.16E+08 '0.'00E+00L9.37E+07':1.48E+07-'1.39E+07 o 1.01E+10 1.35E+10- 4.69E+09 0.00E+0014.59E+09 :1.78E+09 :1.92E+08; d BA-140 1.38E+08. 1.69E+05: 8.90E+06 0.00E+00 5!74E+04' 1;14E+05 2.13E+08' 'j CE-141' CE-144 2.83E+05 1.89E+05 - 2.17E+04 - 0.00E+00' 8.90E403 t00Ev00' 5.41E+08 h 5.27E+07 .2.18E+07 2.83E+06 0.00E+00 21.30E9 7: 0.00E+00, 3.33E+10- ~ [L k PR-143 7.01E+04 2.80E+04, 3.49E+03 0.00E+00 1'63E604: 10.00E+00H2.3GE+08 ~ 1 ND-147 1 3.62E+04 3.94E+04 2.36E+03 0.00E+00 2.31E+04 '0.00E400 kl.42E+08 ~ Units are m* (mrenvyr) per uC1/sec, except for tritium, ;in mrenvyr k per'uC1/sec. ' Table 3-5. Dose Factors for Particulates and= Iodines ' 9 q 3-48 Gen.JRev 7
,O y
.+
i ,U .
.j p E,,h O o' " " '
'^^
y
~ '~~
,.c ,
q ,
}
-rWP-0-M411 !i
, (Gaseous' Effluents-Pathway: VEn" TABLE ,
Age Group!L-CHILD i* Nuclidb Bone. Liver T. Body / Thyroid- ~ Kidney Lung' GI-LLI H-3L. a 00E+00 4.01E+03:~4.01E+03= 4.01E'+03 4.01E+03'~4.01E+03 4.01E+03 : C-14 8.69E+08 11.78Et08: 1.78E+08 1.78E+08':1.78E+08 1.78E+08:- 1.78E+08 A P-32 3. D +09' 1.58E&O8~ 1.30E+08 0. 00E+00: 0.00E+00- 0.00E+00S 9.33E+07 CR-51 0.00Ea0 0.00E+00'.1'.17E+05'iS.50E+04 1.78E+04--1.19E+050 6.21E+06-
.%54 0.00E+(0 .6.65E+08 1;77E+08 0.00E+00 1.86E+08. 0.00E+00: 5.58E+08 FE-55 8.01E+08 :4.25E+08a '1.32E+08 0.00E+00'l0.00E+001 2.40E 8'?.87E+07f FE-59 3.98E+08 6.43E+08 -3.20E+08 .0.00E+00 - 0.00E+00 1.87E+08 6.70E+08: 1 Co-58 .0.00E+00 6.44E+07 : 1.97E+08~ 0.00E+00 0.00E+00 -0.00E+00s 3.76E+08
- i co-60 ~ 0.00E+00 L3.78E+08 1.12E+09 0.00E+00 0.00E+00' 0.00E+00 .2.10E+09 ;
1 i
~NI-63 r3.95E+10:.2.11E+09? 1.34E+09: 0.00E+00 =0.00E+00 0.00E+00; 1.42E+08 L ZN-65: 8.13E+08' 2.17E+09. 1.35E+09 0.00E+00 1.36E+09 ~0.00E+00 3.80E+08-RB FR 89 0.00E+00 4.52E+08. 2.78E+08- 0.00E+00 0.00E+00: 0.00E+00, 2.91E+07J j
'3.60E+10 0.00E+00 1.03E+09~'O.00E+00 0.00E+00 '0.00E+00 '1.39E+09 1
- SA-90 :1.24E+12. 0.00E+00 3.15E+11O.00E+00 0.00E+00' O.00E+00. 1.67E+10 J Y-91 1.86E+07- 0.00E+00 4.99E+05 :0.00E+00 0.00E+00 0.00E+00 2.48E409: M ZR-95 3.86E+06 8.48E+05 7.55E+05':0.00E+00 l'.21E+06 0.00E+00 8.85E+08 i NB-95 4.11E+05 .1.60E+05 1.14E+05 0.00E+00 -1.50E+05 0.00E+00-~2.96E+08' '
KJ-103- 1 33E+07 0.00E+00 5.90E+06 0 00E+003.86E+07: 0.00E+00L: 3.97E+08 1
-RU-106 .7.45E+08 '0.00E+00n9.30E+07.-0.00E+00 1.01E+09- 0.00E+00; 1.16E+10 !
AG-110M 3.21E+07 2.17E+07!-1.73E+07 0.00E+00 4.04E+07O.00E+00. 2.58E+09~ TE-125M 3.51E+08 9.50E+07: 4.67E+07 9.84E+07 -0.00E+00 10.00E+00 3. 38E+08 L ' TE-127M 1.32E+09 ~3.56E+08 1.57E+08 ;3.16E+08 3.77E+09:.0.00E+00; 1.07E+09 TE-129M--8.41E+08. I-131 2.35E+08 1.31E+08( 2.71E+08 2.47E+09 0.00E+00* 1.'03E+09- ,
-1.43E+081.44E+08 8.17E+07 .4.76E+10 2.36E+08 0.00E+00;'1.'28E+07 0 I-133 3.53E+06~- 4.37E+06 1.65E+06 8.12E+08 ;7.28E+06 'O.00E+00)!1.76E+06 .
I-135 S.26E+04 1.13E+05 5.33E+04 9.98E+06' 1.73E+05 .0.00E+00 8.59E+04 l CS-134 1.60E+10 2.63E+10 5.55E+09 0;00E+00 '8.15E+09. 2.93E+09 -1.42E+08-L CS-136 " CS-137 8.24E+07: ~2.27E+08. 1.47E+08 -0.00E+00 1.21E+08- 1.'80E+07- 7.96E+06 2.39E+10 2.29E+10: 3.38E+09< 0.00E+00: _ 7'46E+09: 2.68E+09 11.'43E+08.
. , j BA-140 2.77E+08 2.42E+05 1.62E+07 0.00E+00 17.89E+04 -l'.45E+05 1.40E+08 L
H' 1
-CE-141 l
6.56E+05 3.27E+05 4.86E+04 0.00E+00 _1.43E+05' O.00E+00' 4.08E+08-CE-144 1.27E+0B 3.98E+N 6;78E+06 .0.00E+00 ~2.21E+07L 0.00E+00 l'.04E+10-(1 0 PR-143 ' ND-147 1.46E+05 4.37Ee04 7.23E+03' O.00E+00 2.37E+04-LO.00E+00 1~.57E+08L 1 7.15E+04' 5.797*04_:4.48E+03. 0.00E+00 3.18E+04.'O.00E+00 9.17E+07. 2
/
Units are m'(mrenvyr) pr uC1/sec, :except for; tritium, in mrem /yr 9" per'uCi/sec. ' a Table. 3-5.~ Dose: Factors for Particulaties and Iodines l! l~ j 3-49 Gen. : Rev. 7 ' i lif ; J > l ';
' . ;I
+-I i3 U]<, '
, !) . ,
U-
,,' . ...w..-_
. . m __ ' .
'I
0: '
- z. ,
mP-0-M-011 - l
'. , ' Gaseous Effluents-- '
?.7 CCM10 SITE ANALYSES ,
For radionuclides not determined in each batch or veekly composite - the dose contribution. to the current calendar ' month' or- quarter.- cunnlative summation: may:be approximated by assuming an average. . l monthly or' quarterly concentration. based 'on the previous: monthly ' a or quarterly: composite ' analyses; . The nuclides determined from' composite analyses are H-3,-St-09, Sr-90, and gross alpha.- i 3.8' DOSE P!tOJECTIONS'-
.7 Dose projections shall be made Lat .least once in -.every L 31Edays, . '
based on expected operating ~ conditions. The' projected doses;from. - noble gases and from particulates shall be compared , toi projected dose limits' of 0.2. mrad to air' for gama radiationiL.0.4: mrad .to . 1 0
. air for ~ beta radiation,. and: 0.3 mrem to any organ.i These are
- monthly. dose limits.
4,
.i J
, i l l
-i P
, l, 4
5
- 'f l-t
_. L I J~ 3-50 Rev. l'Oi, l'- 1 , t 4 4 , 4 I . i . , , , , _ . . .
y(E;fg: sp 4
, q w s.
1'- > , l
], ,
PWP-0-M-Oll le l- 1 L I , I i 'in 1 , CHAPTER-4 , y j L 1 i ETTAL DOSE - 1 (Dose' Assessment'-forEnvihonmentalRadiationStandards) 5
'Ihe Radiological Effluent Technical Specification 3.11.4 specifies / 3
- in the Action that when the calculated doses associated-with- the '
- effluent L releases exceed twice the.Elimits ' of ' any one : of J the ' .l Specifications: 3.ll.l'.2, 3.11.2.2 or. 3.11.2.3, . it is : required to prepare and 'subalt ' a- Speciale Report to the ' Comission 'and: limit i subsequent releases. such that the dose or dose comitment to .the
-critical individual from all uranium fuel cycle sources is limited- ' ,".
. to <25 mrem to the -total body :or any organ -(except the; thyroid, i which is limited to <75 mrem) over:12. consecutive months. '
The dose assessment. which' will' be' described in a Special Report, i shall include dose contributions L from direct . radiation from the - ,t! s plant and its components. A variety of techniquesvis(available- !
.for. assessing; this - contribution. A simple i calculation ; may. be, sufficient to demonstrate that the contribution:is unimportant, or!
condit ans ' may? , dictate more complex analyses.
~
. > The ~ most = '
appropriate assessment technique will be determined in thercourse- ' of preparing - the i Special~ : Report and will be e documented in i the - 3 Special Report. t c There are . no 'other uranium' fuel ' cycle ~ sources within ca 50: mile - radius.
;q a
,- Y I
k j o 9- . 4 Gen.'Rev. 7 $ 4
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+
4 2 .i
. '1 .
1 ?, CHAPTER 5
. :i
' RADIOLOGICAL ENVIRONMENTAL MONK 7 AING IDCATIONS ,
f il D Table.'5-1 and Figures 5-1, 5-2, and'5-3 provideLthe' Radiological; - Environmental . Monitor. sg point locations.: ~ i i , =t ( t :(, t
.t 6
t 4' ',1-'
}
. t,
'i q
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it . 1
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'FNP-0-M-011e ;
'J RADIOI.OGICAL ENVIRONMENTAL MONTIORING LOCATIONS -
,m
.(
EXPOSURE PAINNAY SAMPLING LC'JATIONS* < SAMPLE i ic > < AND,4At SAMPLE: IDENTIFICATION-1 J AIRBORNE .
- a. Indicator = Stations: '
Particulates., River Intake Structure (ESE-0.8 miles) .PI: - 0501- [ 3 South Perimeter (SSE-1.0 miles)
.. PI'- 0701 :
- {
Plant' Entrance.(WSW-0.9 miles). PI 1101 -t North Perimeter'.(N-0.8 miles) PI - 1601 ;g i
' Control Stations: , .
{ Blakely, GA (NE-15 miles) PB - 0215 ' Dothan,1 AL ,(W-18 miles): PB - 1218 ! Neals Landing,-FL (SSE-18 miles) : PB - 0718; 1 CoumunityiStations: Great Southern Paper Co.'(SSE-3~ miles) PC -.0703 ichford,1 AL -(WSW-8 miles) PC -;11081 ,
={
Columbia, AL (N-5 miles) PC - 1605' ;
- b. Radioiodine Indicator Stations: .
l River Intake Uructure (ESE-0.8; miles) II'.-. 0501-South'Permiter (SSE-1.00 miles)< II 701 1 - Plant Entrance (WSW-0.9.. miles).- IIi- 1101o North Perimeter (N-0.8 miles) II. - 16011
- (
Control Stations:-
, d Blakely,-GA-(NE-15 miles) -.IB -.0215? .!
Dothan,-AL (W-18= miles) ID -'1218 . Neals Landing, FL-(SSE-18 miles)' -IB - 0718- #
-1
' Community Stations: . . .
t Great Southern Paper Co.l-(SSE-3 miles) IC '0703
;e a
- 2. Direct Radiation Indicator Stations:'
f Plant Perimeter ' E (NNE-0.9 miles) i 1 AI - 0101' ! (NE-1.0 miles) *
- RI 0201 1 (ENE-0.9 miles) RI --0301 (E-0.8' miles) ,
RI - 0401' 'j
'(ESE-0.8 miles) RI -10501-
- (SE-1.1 miles) RI s0601- '
'SSE-1.0 miles) RI - '0701 (S-1.0 miles)!
~RI -0001- ;
a .(SSW-1.0: miles), , 1RI'- 0901 ' (SW-0.9 miles)~ RI. 1101-(WSW-0.9, miles) RI'- 1101 ' i
*DistanceasmeasuredfromthecenterpointbetweenUnit1andUnit2 vent stacks.= '
plant /
*Not required by. Tech. Specs. 'Used as'a spare. station
*Not required by Tech. Specs. Userfor comparison purposes with State ef CA EPD . - ' ' ' ,
-i
- Table 5-1. Radiological t,nvironmental Monitor.ing Locations
' 5-2 y Rev. 10
'x ; ,
'~
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~
' i
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.- c FNP-0-M-011J i
*- i
- RADIOLOGICAL ENVIROt@tEtEAL MONTIORING LOCATIONS 4
EXPOSURE PA1HWAY SAMPLING I4 CATIONS SAMPLE'-~
.AND/OR SAMPLE >
IDENTIFICATION:
. (
(W-0.8' miles)- RI'- 1201 i (WNW-0.8 miles) RI - 1301 1
.(NN-1.1. miles) RI - 1401' (NNW-0.9 miles) RI ~1501:
(N-0.8. miles) RI' .1601; j
, Control Stations L Blakely,.GA,;(NE-15 miles) .RB -10215 Neals Landing, FLi(SSE-18 miles); RB_-.0718 Dothan, AL (W-15 miles); .RB -.1215 .
Dothan, AL (W-18 miles) ' RB -l1218 l Webb, AL (NNW-11' miles?L. RB. 1311 1 Haleburg, ALl(N-12 miles'): RB '.1612 Comunity Stationsi .
'(NNE-4; miles) RC - 0104_ 1 (NE-4 miles) RC '0204 (ENE-4 miles)- '
RC c0304
-(E-5 miles) i RC - 0405
,(ESE-5 miles): RC - 0505' si
'(SE-5 miles)-'
-(SSE-3 miles)'
1 RCL =0605' j
~
1 RC - 0703J '
=(S-5. miles) RC - 0805- q (SSW-4 miles) RC:- 0904-(SW-1.2 miles) RC - 1001-(SW-5 miles).. 'RC ~'1005 '
(WSW ' miles)f LRC - 1104; j" (WSW-8 miles)-
.RC - 1108 (W-4 miles) <
iRC 1204 (NNW-4 miles)_ , ' RC - 1304 (NW-4 miles)' . ERC --1404 (NNW-4 miles), RC - 1504 (N-5 miles) .RC!- 1605 M 3.
~
WATERBORNE Indicator' Station::
- a. Surface.- Great' Southern Paper. . . .
WRI , Intake Structure (River Mile-40) Control Station: 4 a Andrews Lock & Dam =
' Upper = Pier . (River! Mile-47)- '
'WRB
- b. Ground -Indicator Station: ,
" Great Southern Paper- WGI - 07 Co.-' Well".(SSE-4 miles)- b1 pi
~ Control Station: .
Whatley Well1(SW-1.2 miles) WGB - 10 t Table 5-1. Radiological EnvironmentalLMonitoring Locations (con't). , i 1 5-3 iRev. 10
+ , .
+ J
.< -. .g.
., . :w i
- o. ;
i * ' FNP-0-M-011 l p [.. 'l RADIOLOGICAL DNIRONMENDai MCtiTIORING) LOCATIONS l EXPOSURE PA'nMAY SAMPLING IDCATIONS . SAMPLE
?-. c.
' ')
AND/OR SAMPLE IDENTIFICATION; .1 I
- c. Sediment . Indicator Station:' l
.' Smith's Bend-1
'(River' Mile-41) RSI:
-1 P
u : Control Station:.~ l
.Andrews Lock & Dami
- Reservoir -(River Milei47)- '
RSB .: -
..j
- 4. INGESTION
. a.: P41k . Indicator Station:' ~ .
'None (There.;are no milk: animals. .
within 5 miles per'the> ..
~
current land use~' survey). ; Control Station: + Ray Lewis Dairy. . ._
~
~Ashford, AL (WSW-14 miles)1 .MB-1114 '
- b. Fish. . Indicator Station':' .
~
I smith Bend :(River Mile-41)- ~ t Game Fish . FGI ,' Bottom l Feeding Fish FBI- f Control 1 Station:', *
'Andrews Lock & Dami .j Reservoir- (River Mile-47). 0 1
Game' Fish 'FGB, Bottom Feeding Fish ~ FBBj, H,
- c. -Forage. . Indicator Stations . . 1 South Southeast Perimeterl(SSE-1.0 miles)LFIL- 07011
] :
'Nortn' Perimeter (N-0.8 miles)- 'FI --16011 *!
South l Perimeter (S-1.0 miles).L
- Northeast Perimetert(NE-1.0 miles)~
, FIl- 0801: l
- FI - .0201 ~t i
Control' Station:' . . I Dothan,; Alabama'(W-18 miles)E FB - 1218 3 g Alternate forage plots i y I Table 5-1. Radiological Environmental Monitofing Locationsi(con't).l ], L ]o 5-4 Rev. 10 ] 1 t
]
J* RAC10 LOGICAL ENVIRONMENTAL MONITORING 1.0 CAT 10NSi if " -- .
'q pe-0-fi-011; 4 .
(- - rq-Lig
-- - ?,,..
'Q N :-
/l .f 2~
f 7175 WARE s. a
' $PL'i-NORMAL ' 3\ p
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""* ""I
- I/Q = 1.0.10-'8 :
'4
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~ 158 . 4 @{_;-[ . -
j 4 70RA41 SAMPLING ^, AL ftD SAMPLING
- @ [ftD. PARTICUIAft$ 4 IODINE $AMPLING g .
as . .w l
+
. i Fi;;ure 5-1. Airborne Sampitng Locations at Farley 4 3
, Nuclear Plant, O J- '3000 feet '
3-3 tj Rev. 7. Q .n l
- - " - -A -
1 FNP-0-M-011 Rt.DIOIDGICAL DWIRONMENTAL MONIMRING LOCATIONS - 1 i 1 1971 1975.. Men cs oeu ,,,, , I wa. su . n.,es ,
*',... q. I iAs t Q = 10 e it' m m' , ,
s..>.,e m e- - < > s , , . i . . .. a mmo ,
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~
y l l e 16 i 8 jis - . s
... Q"n: // ..i .t '. 0.,,,
t4 - y I headland ' me +
,1' ;.
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' 13 , Cmeme.a
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WWW 3 , j stessa e assessi . k(N(
+ ms a nas - . I
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- 12 t. .g- 4 ;
w:} 8 ( :C- ' g - g i ., . y' ,
- f. .
W5W ( (St p :.A , - .i Slecent 51l 10 SW \ 6 ', aI ' 4 55 s..u, . ., t I "*'"'"" Cetteeseedy - ,
, ist , 0. 4, ,M 1
.. .. estos cauan - _ u.
, .acisse comen i u c; o
.-- ,q .
l i l' 4 I J i e t g /, f
! ! 1 1
- f i g
(. a . ua 4- ' FORAGE SAMPtiNG
& fLO 5AMPtl4G
' g It0 P ARflCULAft1 AND iO0 int SAMPttNG O MILE SAMPtlNG -
rigure 5-2. Airborne Sampling Locations at Farley Nuclear Plant, 0
- 20 miles-
! 5-6 Gen. Rev. 7 - 1 I 1 i 1
. . _ , 4 & . . . - -
. ,j FNP-0-M-011- k
,c RADIOLOGICAL ENVIRONMENTAL MONITORING LOCATIONS '
i 1
.i
)
I
- /-
COLUMeia l n
.i
( ANostws L0ct 4 OAM 1ARL!r t 10 MILis j g.lat PLAN 1l
.. }
-l ' (AaLY county '
i
##- Gioacia -
ASWORD l l _ _ _ _ _ .
. ,i 12 I i !
coRoon ; ; es y NOU570N couMIT - ALAsAMA t
- E
~
INDICATOR STAfl0NS ' CONTROL STAil0NS K suaract AnoGnoumo nAttR '
@ suntact wartR. Fl$N AND $tDiMINT .
X fl$H AND $tOlMENT
@ GRouMO WArtt i l'
I Figure 5-3.. Water Sampling Locations.for Farley Nuclear Plant ' 4 5-7 Rev.'7
. . . . . - ~ _ . , _ - . -
- p. .T g '~ ' ' - - ~ ~ ~
~ '
--------7-~~~-
0
..; . q
- FNP-0-M-011-
.i 4
CHAPTER 6. I METEOROLOGICAL
SUMMARY
l Tables) 6 through! 6-4 ~ provide a sumary of meteorological data - for the years 19711 through 1975. The annual average XM and D/Q . i values- for.the ground level and mixed mode releases- are taken::from this data. ' j The selection of annual average value for site boundary is made by using' the highest value for any sector -(see Table 3-2 for site: ,
' boundary - and ~ nearest receptor distances) . : :The determination of 4 >
annual- average- values :for nearest receptor is made by ' comparing the: X/O and D/Ql: values 'at each near receptor, and _ selecting the. - highest of theselvalues. Near resident locations-are based on the-annual land use; census. The nearest' receptor is at 1.2-miles in-the SW sector, and.is'the same-for the mixed mode and. ground level releases..
.c For the Idata presented in - Tables ' 6-1 through 6-4, the~ annual average X/Q and D/Q values;are:.
Plant Stack (mixed' mode) Site boundary: I 1 (R20), = 1.08 E-6 at SSE, 0.5 0.99 mile- I Nearest receptor: (R70),, = 8.03 E-7 (DM),y = 1.05 E-8 8
)
Turbine Building and ILRT (ground level) q
;i Site boundary: E (220), = 4.87 E-5 at S, 0. 5 - 0.99 mile Nearest. receptor:
] l' (R A),, = 8.74 E-6 '
l (D)Q),, = 2.64 E-8 { l, 6-1 Rev. 10 1 L n d
_ ~_ __ _ FNP-0-M-011 M . Meteorological Summary i FARLEY NUCLEAR PLWT? DISPERSION PARAMETER X/Q FOR MIXED MODE Distance to the control : location, in miles' sector. 0.25-0.5 0.5-0.99' 1.0-1.49 '1.5-1.99. '2.0-2.49
.N. 2.16E-06 9.21E-07 5.92E 3.83E-07. 2.42E-07 NNE 2.35E-06 1.02E-06: 6.18E-07 3.82E-07 2.34E-07 NE- 2.23E-06; 9.61E-07 6.06E-07 3.86E-07
,1,12E-06 2.40E-07.
ENE 5.03E 3.76E-07L 2.65E 1.76E-07 ~ 7 E 1.20E-06 5.21E-07. 3.57E-07 - 2. 45E-07 ;- 1.60E-07.
-ESE 1.55E 6.43E-07f 3.83E-07, 2~.44E-07 1.55E-07.
SE _2.47E-06 9.69E-07 5.52E 3.47E-07 :2.19E-07. SSE 2.77E __1.08E-06 : 6.57E-07 4.34E-07 2;81E-07 i S 2.10;-06 9.37E-07 5.'90E-07 4.09E-07. :2. 74E -SSN: 2.02E-06 8.29E .6.30E-071 ~4.16E-07 2.66E-07' SW 2.05E 8.34E-07 8. 03E-07. -- 5.07E-07 3.16E-07 WSW 1.89E-06 7.41E L7.33E-07 ' 4.66E -2.88E-07 *
.W l'.67E-06 6.74E 15.81E-07f L 4.12E-07 '- 2.53E-07, WNN 1.43E-06 5.97E-07: 4.11E-07: :3.13E-07 2.17E-07 NN 1.32E-06 5.65E - 3. 88E 2.68E-07. 1.77E-07 NNN 1.66E-06 7.21E 4.85E-07 3.23E-07 2.07E-07 t
P Note: Values are based on the joint frequency data between:1971 and 1975. " 1 l _) l l i Table 6-1.~:X/Q Values for the Plant Stack 6-2 Gen. Rev. 7[ l 1. I
-y ,
FNP-0-M-011-
'., .MeteorologicaliSumary
, FARLEY NUCLEAR Pl. ANT
.DISPERS50N'PARAMETERX/QFORMIXEDMODE
.(Continued)-
Distance to the control location, in' miles-Sectorf _2.5-2.99- -3.0-3.49" 3.5-3.99' 4.0-4.49 4.5-4.99, N '1.65E-07 1.24E-07. 1.01E-07 9.11E-08. i te4E 1.55E-07 1.15E-07 9.23E-08: -8.28E-08 8'27E-08'. 7.48E .1 NE- 1.61E-07-- 1.19E-07 9.62E-08 8.63E-08i 7.79E-08> 1 ENE. 1.22E : 9.~28E-08 7. 61E--08 6.88E-08 6.24E-08 ' E' 1.12E-07. 8.54E-08 .7.09E-08' 6.43E-08 5.86E-08 1-
-ESE 1.07E-071 8.13E-08/ 6.75E-08 ~6.12E 5.58E-08 -1 SE. 1.51E-07 1".14E 9.50E-08: 8.61E-08 ,7.88E SSE '1.96E-07 1.50E-07 1.26E 1.15E-07. 1.05E-07^
-1.96E -
S 1.52E 1.'29E-07 1.18E-07" 11.09E l).i
- SSW- 1.84E 1.39E-07 ~1.22E-07. 1.18E-07 :1.08E-07 !
2.13E-07 1,60E-07' SW- 1.30E-07 >1.27E-07 ?1'.15E-07 - WSW _1.92E-07 1.57E-07 1.26E-07' - l'.13E-07; L1.02E -
~
W. _1.68E-07 1.69E-073 l1.34E-07 '1.19E-07 1.08E-07. WNN- 1.74E 1.72E-07 1. 35E-07 -- 1,21E-07 y} l'. 09E-07 ! s NN' 1.37E-07 1.24E : 1.18E-07.. 1.06E-071 19.60E-08 1 NNW 1.42E-07 1. 07 E-07. -. 1.04E 9.36E-08 : 8. 50E ;
-Note: Values are based on the joint frequency data between 1971 and 1975.
~
[ j l
. i i
Table 6-1. XA) values for the. Plant . Stack (Continued) , 6-3 Gen. Rev. 7 !
;s.
l FNP-0-M-011~
~
Meteorological Stumnary ,
' l.
FARLEY NUCLEAR' PIANT DISPERSICN PARAMETER X/Q'FOR: GROUND LEVEL: RELEASES , Distanca to the control location, An miles 1 Sector. 0.25-0,5- ~0.5-0.99- '1.0-1.49 1.5-1.99 ~ -2.0-2.49 N 7.25E 2.38E 8.63E 4.02E-06 2.05E NNE 6.16E 2.02E-05 '7.32E-06 :3.39E-06 1.73E-06 'l NE 5.86E-05 1.94E-05. 7.04E-06. 3.24E-06 1.65E-06 ; ENE 5.27E-05. 1.74E-05 6~32E . 2.92E-06 1.49E-06
~
E 6.28E-05. 2.02E-05 7.'27E-06 ~ '3.40E -.1.75E-06 ESE 16.18E-051 -1.97E-05: '7.09E-06 '3.33E 1.72E-06 SE , 9.48E-05, 3.01E-05: '1.07E-05 5.06E-06 2.63E-06' SSE 1.44E-04 4.55E-05 1.61E-05 '.7.65E-06 3.99E-06
.S~ :1.55E-04 4.87E-05 1.72E =8.20E-06 4.28E-06
'SSW 9.78E-05= 3.12E-05: '1.11E 5.23E 2.71E <
SW 7.40E-05 2.40E-05 8.74E-06 4.05E-06. 2. 07E-06 -- WSW 6.01E-05'- 1.97E-05 -7.18E-06< 3.31E-06
-1.68E-06 W- 5.76E 1.88E-05 6.79E-06 3.14E-06' !1' 60E-06 :
WNW 5.55E-05 -1.82E-05 6.55E-06 ~3.03E-06' l'.55E-06 NW 5.67E-05 1.86E 6.76E-06e 3.14E-06. 1.60E NNN 6.60E 2.16E 7.85E-06 '3.65E-061 -1.87E-06i Note: Values are based on the joint frequency data;between 1971l [ and 1975. l 7 l V l j, l ,o Table 6-2. X/Q Values for Ground Level Releases 4 Gen. Rev.'7 l' . 1 l l-E l1 i l' i
.s .
' l- g; .g
.. .FNP-0-M-011
;, . Meteorological Summ3ry t i
FARLEY NUCLEAR PIANT " q
' DISPERSION PARAMETER X/Q FOR GROUND LEVEL . RELEASES' i, (Continued)'
Distance to the control location,'.'in miles Sector 2.5-2.99 3.0-3.49- 3.5-3.99- ~4.0-4.49- 4.5-4.99 - N- 1.19E-06' 8.24E-07' 6.09E-07 5.35E-07) 4.71E-07
-NNE 1.00E-06 -6.94E-07' 5.13E-07 {
.4.50E-07' :3.96E-07
'NE: 9.47E-07 6.54E-07 '4.82E-07 4.23E 3.71E-07>
ENE 8.56E 5.92E-07 4.37E-07: 3.82E-07J 3.37E-07 t E 1.02E-06' 7.08E-07 v 5.24E-07 4~61E-07 4.06E-07 ESE 1.02E-06' 6.99E 'i
- 5.18e:-07 4.56E-07' 4.02E SE 1.54E-06 .J.07E-06 7.99E-07: 7.04E 6.20E-07 SSE 2.34E-06 !
1.64E-06.- -l'22E-06~
. 1.08E-06 9.49E-07' S 2.51E-06' 1.76E-06 1.31E-06 .1.16E- 06 . >1~02E .
SSW 1.58E-06 1.105-06: 8.17E 7.19E-071 6. 33E- 07 i
-SW 1.20E-06 8;30E-07 6.12E-07 5.38E-07~ .4.73E-07 WSW 9.65E-07 6.67E-07 4.91E-07a ,4.31E-07 '
3.79E-07 W 9.20E-07 6.'37E-07 4. 71E-07 .-
~
4.13E-07' -3.63E WNW 8.92E-07 6.18E-07 4.56E-07 4.01E-07 .3.52E-07' i NW 9.25E-07 6.41E-07 4.73E 4.16E-07 ~3.65E-07 NNW 1.10E-06 -7.50E-07 5.54E-07 4.87E-07 . - 4. 28E-07 Note: Values are based on thel joint frequency data between 1971' ' and 1975.
.t il
;^$
Table 6-2. X M Values for Ground Level Releases (Contihued)~ 6-5~ Gen. Rev. 7 1 1 n
g
?!?
L . L
-FNP-0-M-011 ~
, Meteorological Summary.
u FARLEY NUCLEAR PLANT - DEPOSITION PARAMETER D/Q FOR MIXED MODE . Distance to the control location,!in miles- ,. p Sector - .0.25-0.5 0.5-0.99- 1.0-1.49 1.5-1.99 2i0-2.49
~
l N -3.82E -1.78E-08 7.53E-09 3.39E-09~ 1.62E-09 .. l i NNk. - 4.57E-08 2.08E-08 8.69E - 3.88E-09 1.85E-09. i NE 4.78E-08 ,2.20E-08 9.08E-09 4.03E-09 1.92E - ENE 2.67E-08 1.32E-08' 5.63E-09 2.54E-091 1.22E .> E. 2.87E-08. I'.40E-08 5.77E-09 2.55E '1.22E-09 ESE 3.29E-08 1.53E-08 6.17E-09 2.70E-09 1.28E-09 SE 5.30E-08 2.37E-08 9.31E-09' 4.01E-09~ 1.90E SSE .5.07E-08. 2.35E-08 9.53E-09 4.19E-09' -1.99E-09n- 'I S 4.86E-08 2.29E-08 9.16E-09 4.00E-09 1.90E-09 ,! SSW i 4.29E-08. 2.10E-08 19.09E-09' . 3.97E-09: 1.88E-09= SW . 4.70E-08 2.28E-08 ~1.05E 4.39E-094 2.04E-09 - l WSW 4.46E-08 2.17E-08' 9.88E-09 - 4.12E-09 1.92E-09. W 3.96E-08 .1.94E-08 -8.39E-09 WNW 3.63E-09 :1.70E-09 : 3.22E-08.' 1.56E 6.35E-09 2.85E-09 -1.37E-09 NW 2.83E-08 1,35E-08 :5.55E-09 2.46E-09 NNW 3.24E-08 '1'18E-09 1.55E-08 6.59E-09
~
- 2.97E-09 1.42E-09 1 Notet Values are based on the joint frequency data between 1971-and 1975. ~
1 s 1 1
~J i
l l ll
.,i Table 6-3.-D/Q Values for the Plant Stack ,t l
6-6 Gen. Rev. 7 3 l' t
. = n__ = __._ - - -_ -____ _ __
, . . . r
'FNP-0-M-011-Meteorological Sumary ,
~
i i FARLEY NUCLEAR PLANP DEPObITION PARAMETER DA FOR' MIXED MODE (Continued)' Distance to the control locationb in mil'es? Sector 2.5-2.99J 3.0-3.49. 3.5-3.99 4.0-4.49' -4 5-4'.99 l N - 8.71E 5.64E-101 '3.10E-10 3.37E-10 2.91E-10 mt 9.91E -6.43E-10. 4.44E-10= -3.82E-10. 3.30E-10
- NE -1.03E 6.65E-10 4.62E 3.98E-10 13.43E-10>
DIE 6.57E 4.22E 2. 96E-10 .- 2.55E-10 -2.20E z E' 6.57E 4.20E-10 2.96E-10 '2.55E-10 2.20E-10' ESE 6.88E-10 4.40E-10) 3.09E-10 2'.660-10;- 2. 29E-10 _- SE l'01E 6.48E-10 4.55E-10. c3.90E-10e 3.36E-10; SSE- 1.07E-09 i
- 6.85E-10
- 4.79E-10 '4.12E-10F 3.55E !
S 1.02E-09 6.4S;:-10, 4.59E-10~ '3.94E-10_ '3.40E-10
-SSW 1.00E-09' 6.41E 4.50E-10 3.86E 3.32E-10. '
SW 1.08E-09 6.90E-10' .. 4,81E-10: :4.12E-10 '3.53E-10e
- WSW 1.02E-09 :6.51E-10l 4.53E-10 i3.87E 3.32E-10t W~ 9.00E-10 5,92E-10. 4.13E-10 13.54E-10 3.04E-10" NNW :7.33E-10 4.95E-10 3.52E-10 3.05E-10 NW 6.37E-10 4.11E-10. 2.65E-10( q 2.91E-10 2.50E-10: 2.14E-10 '
NNW 7.66E 4.95E 3.45E-10 '2.97E-10 2.56E-10' i
~
Note: Values'are based on the joint frequency data between'1971! 3 ! and 1975. y
,I
!l
.y 1
~
i i Table 6-3. DM Values -for the Plant Stack (Continued):
-l 6-7 ^ Gen. Rev. 7 , -1
.I
!FNP-0-M iO111
'MetCorologic1 Summary I t
FARLEY NUCLEAR PLANT i DEPOSITICN PARAMETER DM FOR GROUND LEVEL RELEASES Distance to the control location, in miles " Sector. 0.25-0.5- 0.5-0.99 1.0-1.49 1.5-1.99 2.0-2.49 ! N 2.50E-07 7.84E 2.53E-08 9.61E-09 4.28E-09' NNE '2.48E-07 7.77E-08 2.51E-08 9.53E-09 4.24E-09' ' NE 2.~ 49E .7.80E-08' 2.52E-08 9.57E-09. 4.26E-09 4 ENE 1.69E-07 5.29E-08 1.71E-08 6.48E-09 2.88E-09 E 1.69E-07 5.28E 1.71E-08 6.48E-09 ! 2.88E-09' ESE 1'.80E 5.54E-08 1.79E-Or, 6.80E-091 3.02E-09: J SE 2.752-07 8,63E-08 2.79E-08 1.06E-08: '4.71E-09 SSE 3.66E-07 1.15E-07. 3.71E-08 1.41E-08, 6 25E , S 3.70E 1.16E-07 3.75E-08 1.42E-08 6.33E-09 ! ssW 2.75E-07 8.62E-08 2.79E-08 1.06E-08. 4.70E =i sw 2.60E-07 8.15E-08 .2.64E-08 '1.00E-08 ' 4.45E-09' WSW 2.31E '7.24E-08' ~2.34E-08; 8.88E-09l 3.95E-09: ' W 2.11E-07 .6'61E-08 2,14E 8.11E-09 3.61E-09
- WNW 1.83E-07 ,5.73E 1.85E-08 7.02E-09 3.12E-09 !
' NW 1.74E-07 5.45E-08 1.76E-08 6.68E 2.97E-09 i NNW 2.13E-07 6.67E-08 2.16E-08. 8.19E-09 3.64E-09' s i
Note: Values are based on the joint frequency data between 1971 e and 1975. - A
, d 1
i k i s e Table 6-4. DM Values for Ground' Level Releases
" l.
6-8 Gen. Rev. 7
, 1 l
- l. .
4 l l c 1
? 1
' , j 3 . .
- ~ '
f
','5 ,
if FNP-0-M-011-
. MetOorologichl' Sununary -- !
, FAP1EY NUCLEAR PLANT l DEPOSITION PARAMETER D/Q FOR GROUND LEVEL RELEASES-
'(Continued) l Distance to the control location, in.milesi i
sector 2.5-2.99 3.0-3.49. 3.5-3.99 4-0-4.49'
. 4.5-4.99 !
N mE 2.22E-09 1.45E-09 '9.79E-10 8.27E 6.99E-10 I 2.20E-09 1.43E-09 9.71E-10 8.20E-10: 6.93E-10 a NE- 2.21E-09 1.44E-09 9.75E-10' 8.23E 6.96E-10 ENE 1.50E-09' 9.76E-10z 6.60E-10 5.58E-10 4.73E-10a
)
E 1.50E-09' '9.75E-10: 6'.60E-10 5.57E-10.- 4.71E-10 ESE 1.57E-09 li02E 6.72E-10 5.85E 4.94E-10 SE 2.44E-09' 1.59E 1.08E-09 . 9.' 11E .7.70E-10 SSE 3.25E-09 2.12E-09' -}' 1.43E-09 1.21E-09, 1.02E-09 S- 3.29E-09 -2.14E ;1.45E-09 -1.22E -1.04E-09. ' SSW 2.44E-09~ 1.59E-09 1.08E-09L 9.10E-10 7.69E-10' SW 2.31E-09 .1.51E-09 '1.02E-09 ' :8.60E-10. 7.27E-10 Wsw 2.05E-09 1.34E-09 9.04E-10 7.64E-10 6.46E-10
- W '- .
1.87E-09 1.22E-09 L8.25E-10' 6.97E 5.90E 1.62E-09; WNW l 1.06E-09 7.15E-10 '6;04E-10= - 5 ~.11E-10 NN 1.54E-09 '1'.01E-09 6;80E-10 5.75E-10: 4.86E-10 NNW 1.89E-09 1 l'.23E-09 8.34E-10 7.04E-10' 5.95E I-Note: Values are ba:*d on the joint frequency data between 1971 and ' 1975. 1
.4 It i
l 1
~
Table 6-4. D/Q values for Ground Level Releases (Continued)
- r 6-9 Gen. Rev.-7 !
I m y
.5 :,
I FNP-0-M-011 L., . - * ',- . l-- \\ .
-?
t. l- , l l APPENDIX- s ODCM EQUATIONS AND SOURCES i t il
'Ihe equation number used in the textcis indicated,' along lwith the - .
equation and an. explanation of the origin- of the, equation. Terms and factors are not defined here . since they are - described in = .' detail'in the text.. . +
-r Equation- Origin !
1
- 2.1 C , ,
t ,_ * . 'g 1-
- iL MPC g ,
This' is, the equation that must be' satisfied to ' meet :1 10CFR20, Appendix B,LTable II, Column 2irequirements at. (
'the discharge: point of the site.
2.2 2 :I C ;, u , p
- f ,u p -.
g' ' ' ,. g
.u-1 u
This- equation is- the. derived: ' concentration 'of , radionuclide, - i, at the - site boundary considering . all' liquid pathways discharging radioactive water. - l _- 2.3 I I C ,,,,
- i f,,,
O i F, a L:
$1 .
MPC- 1 This .is the requirement for multiple release pathways ' to meet 10CFR20 concentration limits.- i i A-1 Rev.-10, I
.a
. 5 - - - - . . . - . . _ , _ . + . . . . & w .
\. ' ' ' } f ' L .'L ' FNP-0-MiO11I
, ODCM Equations.and Sources
- b Equation origin-
-2.4' .C , ,. ,
- f ,, ,
i
.g ,
- t. T
- f AP,,, ,l
-MPC, '
This:. defines the pathway apportionment. factor with the restriction.of equation 2.5.
- 2. 5 ~' I Ar,,, $1 ~
p
'the sum: of: the . apportionment factor. shall' not exceed: L onei Requirement to meet 10CFR20 concentration limits.
2.6 1 C,,,.
" E i, j D8% , p !
' AF, , p .i E 1 This is the definition of the minimum dilution fa'ctor required for the pathway-to meet 10CFR20 concentration limits.
2.7 Dr , , = 2
- Dig , ,
- This is the definition of the. required dilution factor.
The' factor of 2 is the safety-factor. 3
+
2.8 2 C ,,,, 1
= I D r" ' '
AF,,, i. MPC, This ' is the formula used:to calculate 'the minimum. required dilution factor. 2.9 Da - Dr Mu ,p = fC,,,,,1 This is the definition' of the monitor setpointi in :the
, i:
units of C1/ml. ( 2.10 SPCy,,_= E,
- M,,, + By ,, l This is the derived monitor- setpoint' in the units of 1 Cpm.
'l A-2 Rev. 10 l
l
,l
}
. .. , ., . . - ~.. . --
~ ~ ^ ~ - - ~ ~
.. . . 3 s-. . ;;
- . .. :FWP-0-M-011-
- ODCM Equations and Sources g Equation Origin :: '
2.11 D, = I ( A ,,1I 6t C3 3 . F[] g 3 L i - This is the' definition of the dose to an. organ, T,sfor , each liquid release. Taken from NUREG-0133, page 15.. 2.12 f, , , - 3 Il r, * . 5 . This is' : the definition ' of .the ' near _ field .. average dilution factor. for each ' release pathway. - Adapted from NUREG-0133, page 16,
-f 2.13 A,, = K; (U, Br + U,' CF, y ] . Driy.
i I This is the organ, T, dose comitment- factor taken from- [ NUREG-0133, page 16 with invertebrate and drinking water deleted and irrigation-vegetable consumption from Reg. Guide 1.109 adapted from equation A-13.
~
2.14 r (1- e- *" '*) f* B" (1-e~*'* ) CF , = M I g
+ e' ;
Yv_ .$1 .P A_3 _ This is the3 equation- that defines the concentration of radionuclide,1, in vegetable, v, i from the irrigation of crops .with contaminated river water. Adapted from Reg. Guide 1.109 equation A-8.and-A-9.-- t 2.15 CF, = M Equation for tritium adapted a from: Reg. Guide' 1.109 equations A-10 and A-9. 3.1 X/O = [(1-E)(X/0),3,y + E(X/Q)q,,] I This is the algebraic equivalent _ of Reg. Guide.1.111 (Ref. 3) statement following equation-(8):-
. . . elevated release 100(1-E ) percent 'of the time and as a ground release E percenkofthetime."
g 3.2 This equation is the same as 3.1, but with D/0 instead of X/Q.- , t
- i. }
A-3 Rev. 10 e
- - M . , . , i i-
_z_.______. ____.____._._.____M_______ .
4 '
~'
- 9. .
i FNP-0-M-011 ODCM Equations and Sources
, . Equation. Origini .i 3.3 E=1 if (W,fu) f 1 or'h,75 hy ,
E=2.58-1.58'-(W/u) if- 1'< (W,fu)~$ 1.5= I l E=0.3-0.06_(W/u) if. -1.5<(W/u)~f5.0 E = 0- ifL (W/u)>5.0 - The equations for E' are L taken from; Reg.. Guide L1.111 , equations (6),-(7), andl(8). 1 3.4 (x/Q)3,y = 2.032 k; / (b3 r, I,)-. . .
- This is Reg. Guide 1.111 equation'(3),'with h - 0_for a ground; release. Also,.in this. equation 1x h,as-become-r , the index i . is' dropped from 6, and- N and .ng' are
-taken care of in the sum over j, f,.and v. '
k, is. added according to .the discussion fo11'owing equation (3) in Reg._ Guide -1.111, (March, .1976): (Ref. ' 2)-' - page_1.111-9:
"(1) Sites in open terrain ... multiply'bv open terrain.- !
correction factor (f'ig. 2)'_' 3.5 I, =-(c', + 0.5h*y /n)*/' ( This is Reg. Guide 1.111 equation (9).. 3.6 I, f (3)1 o, i Li This.is Reg. Guide 1.111 equation (9),-second part;
.-((h,/a,)'/2] 'i 3.7 (x/Q),1,y = (2.032 k,/(L,3,y r, e,.))-e -
t This=is Reg. Guide 1.111-equation-'(3),:with bhanges as noted above for equation 3.4, and e =instead of I , according L to the 'coment iin Reg. Guide,1.111 with the, , I,.- y definition of .! ' 3.8 h,,, h + hy --h, - c L This is Reg. Guide 1.111 equation (4).- l A-4 Rev. 10 ._, 1 i i
, , , - . .- . . _ _ . . ..J- ,
~ _ ._ --
.4
.. ~
PNP-0-M-011
< ODCM Equations.and Sourc2s Equation 1 Origin-3.9 e=3(1.5-W/u,1,y)d
, h is is Reg.' Guide 1.111 equation (5)..
, 3.10 h,,=1.44d(W/u,3,,)*(r,/d)2 _
This isL from Briggs, Plume Rise, .(Ref. 5) L ' equation - 4.33, page 59.
~3.11- h,,<'3'(W/u,1,,)d-Wis is from Briggs, Plume Rise, equation 5.2,.page 59, 3.12 h,,<1.5_(rfu,1,g)*'3 - s-*'C'if S > 0 This is .from Briggs, Plume Rise, . equation 4.28, ' page
- 59. - However, -note in the discussion following that equation that since - there . isL no data - to support ? the -
-theory, the ">" sign in the equation shown'in. Briggs is;.o changed to a "<" sign, using the expression as a upper limit to be conservative.
3.13 r, = (p,/p) W', (d/2)* This 'is'.. from Briggs, Plume Rise, ~ equation 4.19b, page- :
~;
27. 1 3.14 S = (9.8/T) (oT/oz + 9.8 x 10~3). 1 i S~= stability parameter from Briggs, Plume Rise,, equation 4.16,:.page 27,
+
S = (g/r) (80/8z) ;l 1 80/8z = dT/8z + 9.8-deg C/Km: ! y This latter expression is,from Meteorology and iAtomic i I Energy' . (Ref. 6), page .192, in! the: text. following: equation-(5.9). } a n
"' The units in equation 3.14':are oz in m and temperature i
H in deg K. (g = 9.8 nVsec' squared) b '! Li i o
?
.A-5 Rev. 10 f
i 1 H . y . 1
q .,_
- 3
, a- . s 4 t -
FNP- D-M-011 ( 00CM Equations 1and Sources-- , l I Equation origin' , i
' \
3.15 . (D/Q)gy j = k,f,6fyg_(0.3927Lr,)~ i This .is 'for ground releasesi-and is from Reg. Guide 1.111, page.12, in the ~ section on Dry Deposition. The- . relative _ deposition rate (6 - is multiplied by the
. fraction of the release in t$al) sector (f,) and divided .
by the cross _ wind distance' 1 Since the sector is 22.5 degrees wide (0.3927 radians), ; the: cross wind distance'is_0.3927 r, at distance rg.. 7
.L k, is.as;given'in equations ~3.4 and 3.7. .
3.16 -(D/Q)3,,]=k,'f,8,yg/(0.3927rg) This. is for elevated releases, and the ' development is, # the_same:as for equation'3.14.. P 500 mrenVyr F, ! 3.17 I, K Q,<g i (XA)), x F . v This is derived from NUREG-0133 equation on_page 22 for-noble gases, whole body dose. ' j ~ 3000_mrenVyr F, 3.18 E, (L, + 1.1M ) 0 , < 1 3 1 s (X/Q)y x: F ' 1 This'is derived from NUREG-0133 equation on page:22 for-noble gases, skin dose, t 500 mrenVyr F, l 3.19 Q, _ = (X/Q), x F x K1 This is derived from equation-3.18, 3.20 S, = E,(Q,/F,) + b . This is from a units conversion of'Q, in equationL3.19 to cpm, plus. background. i h- < { l , a A-6 -Rev. 10 1.
.I I
y 1
- . _ _ . - . _ _. .. . . L- - .. ::.
f :. - ... .
.. n 7 Q. ?
FNP-0-M-011-
. :. ODCM Equations and' Sources Equation- Origin ;
j 3.21 St = E,(Qt /r,) + b , Wis~is equation 3.20 for_a specific case. I q 3.22' I, Ki I,- [(R C), 0 , ) < 250. mreer 1 I l his is NUREG-0133 organ dose;isquation~ from. page 22, l with V = 0, and .with unit; dose rate: limit equal to halfofsitelimit.~ 1 3.23 I,(Li + 1.1M r). . ,Il[(K), Qi, ), < ;1500 mrenVyr - Wis is ' NUREC- 1033 L organ dose equation from page - 22,; with V = = 0, we with unitj dose rate . limit- equal to halfol'sitelimit. ' 3.24 I . I, Ej - [Pi, i W,, Qiy).< 750'mretyyr
.i his is NUREG-0133 ' organ ' dose equation ' from page .22, with W -. = 0, and with unit - dose rate : limit equal to
, )
half of site Elimit. Also, it Mis:: sumed ' over all' pathways, as indicated.in the definition of'P .. i 1! 3.25 D, y - L 14 x 10-
- ii I M I3 at ,I (X/Q)gy Q 3 i ,y V
3.26 D., = 1'.14-x 10'* E N Ij l At3 I'(X/Q)3,, Qi3y i i ,
- v -.
Equations 3.25 and converted to- hour 3.26- are' NUREG-013}, page '28, becomes 1.14 x 10'}y1/hr/ values. 3.17 x 10' 1/sec/ year year.- B, = 0 and bi = 0. ; t
~A-7 Rev. 10 w,
m :. k' ., i I l ; .
.. FNP-0-M-011 g .
ODCM Equations and Sources Equation Origin: t
-3.27- D,=3.17x10[M, E (K4)), y-
_Q, 3 ; a
, \
3.28 D,=3.17.x10[Ng E (X7Q),.'Q,y -l v --
-(
~
Equations 3.27 and 3.28 .are from NUREG-0133,- page 28, . with Bg.- O and b - 0. i ; 3.29- D,,, = 1.14~x:10 . I, ' I, f,, R ,, , ' I) ~ ot, Iv . . [ W,3, 3 13 D,) , This is from NUREG-0133, ' page~ 29, with time in hours, ! and W, - 0.and w - 0. 3.30 D,, - 3.17:x 10'# E~E R,',,,'E W, Q3y - i_ p v -r
- s, This is-from NUREG-0133p page.'29 again, with W, = 0 and w, = 0.
j P s.>
=
- 't c
'y
'i
-i
'i
+ l s A-8 :Rev. 10 ; i l-
, . - - . ._,2.. -
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