ML20094R863

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Offsite Dose Calculation Manual for Enrico Fermi Atomic Power Plant Unit 2
ML20094R863
Person / Time
Site: Fermi DTE Energy icon.png
Issue date: 05/31/1984
From:
DETROIT EDISON CO.
To:
Shared Package
ML20094R836 List:
References
PROC-840531, NUDOCS 8408210085
Download: ML20094R863 (119)


Text

,-

WFSITE DOSE CALCULATION MANUAL 7,

OETROIT EDISON COWANY ENRICO FERMI ATOMIC POWER PLANT - UNIT 2 MAY 1984 8408210085 040725 PDR ADOCK 05000341 P

PDR ODCM, Fermi-2 2766ei/0051n, 05/07/84

1 TABLE OF CONTENTS List of' Tables...........................

List of Figures............................

iv V

References.............................

vi Introdwtion.............................

.l.0 LIQUID EFFLUENTS 1.0-1 1.1 Liquid Effluent Monitor Setpoints 1.14 Liquid Radwaste Effluent Line Monitor.........

1.0-1 1.1.2 Circulating Water Reservoir Decant Line Monitor....

1.0-6 1.0-9 1.2 Dose Calculaticp fm Liquid Effluents 1.2.1 Dose to Critical Receptor Due to Fish Consumption...

1.0-9 1.2.2 Dose Due to Fish and Drinking Water Consuiption....

1.0-11 1.2.3 Methodology for Individual Liquid Dose Projections...

1.0-21 1.3 Definitions of Liquid Effluent Terms............

1.0-23 1.4 Liquid Radioactivity Monitwing System...........

1.0-27 2.0 GASEOUS EFFLUENTS 2.1 Gaseous Effluent Monitor Setpoints.............

2.0-1 2.1.1 Reactor Building Exhaust Plenun, Standby Gas 2.0-1 Treatment System, Radwaste Building Ventilation, Turbine Building ventilation, and Chaite Storage Building Ventilation Radiation Monitors 2.1.2 Containment Drywell P w ge...............

2.0-3 2.2 Gaseous Effluent Dose Rate and Dose Calculations......

2.0-7 2.2.1 Unrestricted Area Bomdary Dose Rate 2.0-7 2.2.2 Unrestricted Area Air Dose and Dose to Individual...

2.0-9 2.2.3 Methodology for Gaseous Dose Projections........

2.0-22 2.3 Meteorological Model....................

2.0-53 2.0-53 2.3.1 Atmospheric Dispersion 2.3.2 Relative Deposition..................

2.0-56 2.4 Definitions of Gaseous Effluents Parameters 2.0-67 2.5 Gaseous Radwaste Effluent System and Ventilation Exhaust..

2.0-72 Treatment System (DCM, Fermi-2 2766W/0051W, 05/07/84 i

TABLE OF CONTENTS (Continued) 3.0 RADIOLOGICAL ENVIRONENTAL MONITORING PROGRAM 3.0-1 3.1 Sampling Locations.....................

3.0-10 3.2 Interlaboratory Ccaparison Program.............

4.0 TOTAL DOSE FROM URANIUM FUEL CYCLE 4.1 Calculation of Total Dose from Uraniun Fuel Cycle......

4.0-1 l

l l

I l

ODCM, Fermi-2 11 1

2766W/0051W, 05/07/84 l

l I

LIST OF TMILES Table No.

Page No.

I 1.0-14 1.2-1 Bioaccumulation Factors.................

1.2-2 Adult Ingestion Dose Factors............... 1.0-15 1.2-3 Site Related Ingestion Dose Commitment Factor (Ag)

(Fish Consumption)................... 1.0-17 1.2-4 S&$e Related Ingestion Dose Commitment Factor (A'g )

(Fish and Water Consumption).............. 1.0-19 2.1-1 Dose Factors for Exposure to a Semi-Infinite Cloud of 2.0-5 Noble Gases......................

2.1-2 Geseous Release Pathway Flow Rates............

2.0-6 2.0-25 2.2-1 Inhalation Dose Factor for Infant 2.2-2 Inhalation Dose Factor for Child............. 2.0-28 2.0-31 2.2-3 Inhalation Dose Factor for Teenager 2.0-34 l

2.2-4 Inhalation Dose Factor for Adults 2.2-5 Ingestion Dose Factor for Infant............. 2.0-37 2.0-40 2.2-6 Ingestion Dose Factor for Child j

2.2-7 Ingestion Dose Factor for Teenager............ 2.0-43 2.2-8 Ingestion Dose Factor for Adults............. 2.0-46 l

2.2-9 External Dose Factors for Standing on Contaminated Ground. 2.0-49 2.2-10 Individual Usa.ge Factors................. 2.0-51 2.2-11 Stable Element Transfer Data............... 2.0-52 2.3-1 Open Terrain Recirculation Factor............. 2.0-57 3.0-1 Radiological Environmental Monitoring Program - Sample..

3.0-2 Locations and Associated Media 1

0D04, Fermi-2 111 2766W/0051W, 05/07/84

LIST OF FIG.RES Figure No.

Paae No.

1. 0.-1 Example Calibration Curve for Liquid Effluent Monitor 1.0-8 1.4-1 Liquid Radioactivity Monitoring System.......... 1.0-28 2.3-1 Vertical Standard Deviation of Material in a Plume (aZ) 2.0-58 2.3-2 Plume Depletion Effect for Ground-Level Releases..... 2.0-59 2.3-3 181ume Depletion Effect for 30wn Releases......... 2.0-60 2.3-4 Plume Depletion Effeet for 60wn Releases......... 2.0-61 2.3-5 Plume Depletion Effect for 100-m Releases 2.0-62 2.3-6 Relative Deposition for Ground-Level Releases 2.0-63 2.0-64 2.3-7 Relative Deposition for 30an Releases.......,...

2.0-65 2.3-8 Relative Deposition for 60Mn Releases 2.3-9 Relative Deposition for 100wn Releases.......... 2.0-66 2.5-1 Gaseous Radwaste Effluent System............. 2.0-73 3.0-1 Radiological Environmental Monitoring Program 3.0-7 Sampling Locations By Station Number 3.0-2 Radiological Environmental Monitoring Program 3.0-8 Sampling Locations By Station Number (Greater than 5 miles) 3.0-3 Radiological Environmental Monitoring Program 3.0-9 Supplementary TLD Stations By Station Nunber 1

0004, Fermi-2 2766h/0051W, 05/07/84 iv

\\

References 1.

J.

S.

Boegli, R.

R.

Bellamy, W.

L.

Britz, and R.

L.

Waterfield,

" Preparation of Radiological Effluent Technical Specifications for Nuclear Power Plants", MJREG-0D3 (October 1978).

2.

Calculation of Annual Doses to Man from Routine Releases of Reactor Effluents for the Purpose of Evaluating Compliance with 10CFR 50, Appendix I, U.S. EC Regulatory Guide 1.109 (March 1976).

3.

Calculation of Annual Doses to Man from Routine Releases of Reactor Effluents for the Purpose of Evaluating Compliance with 10CFR 50, Appendix I, U.S. EC Regulatory Guide 1.109, Rev.1 (October 1977).

4.

"Envircrvnental Report, Operating LJcense Stage", Detroit Edison Company, Fermi-2 Plant.

5.

" Final Safety Analysis Report", Detroit Edison Company, Femi-2 Plant.

6.

Methods for Estimating Atraspheric Transport and Dispersion of Gaseous Effluents in Routine Releases from Light-Water-Cooled Reactors, U.S. NRC Regulatory Guide 1.111 (March 1976).

7.

Development of Sector-Specific Recirculation-Stagnation Factor for Meteorological Data Collected at the Enrico Fermi Atomic Power Plant, Unit 2, Project No. 3020, Camp Dresser & McKee Inc.

Environmental Sciences Division, Septanber D,1978.

8.

Methods for Estimating Atmospheric Transport and Dispersion of Gaseous Effluents in Routine Releases from Light-Water-Cooled Reactors, U.S. EC Regulatory Guide 1.111, Rev.1 (July 1977).

e E)CM, Fermi-2 2766W/0051W, 05/07/84 v

INTRODUCTION The OFFSITE DOSE CALCULATION manual is a stpporting docunent of the RADIO-LOGICAL EFFLUENT TECHNICAL SPECIFICATIONS.

As such the 00CM describes the methodolog ' And parameters to be used in the calculation of offsite doses due to radioactive liquid and gaseous effluents and in the calculation of liquid

.cd gaseous affluent monitoring instrunentation alarm / trip setpoints.

The 0004 contains a list and graphical description of the specific sample loca-tions for the radiological environmental monitoring program.

Schematic configurations of liquid and gaseous radwaste effluent systems releases to unrestricted areas are also included.

The 00CM will be maintained at the plant for use as a reference guide and training docunent of accepted methodologies and calculations.

Changes in the calculational methods or parameters will be incorporated into the ODCM in order to assure that the 00CM represents the present methodology in all applicable areas.

Computer software to perform the described calculations will be maintained current with the 00CM.

l l

l l

00CM, Fermi-2 1810W/0051W, 05/07/84 vi f

SECTION 1.

LIQUID EFFLUENTS l

The Enrico Femi Atomic Power Plant, Unit 2, is located on Lake Erie which angsplies make-up water to the Circulating Water System and receives decant l

from the C11tulating Water Reservoir.

All releases from the Liquid Radwaste l

System are to the Circulating Water Reservoir decant line.

i l

1.1 LIEJID EFFLUENT MONITOR SETPOINTS The calculated liquid monitor setpoint values will be regarded as upper bounds for the actual setpoint adjustments. Setpoint adjustments are not required to l

be perfomed if the existing setpoint level corresponds to a lower count rate than the calculated value.

The actual monitor netpoint, which corresponds to the calculated concentration plus background for the specific monitor, is detemined from calibration data or from operational data associated with liquid sample analysis data. (See Section 1.1.1).

l 1.1.1 LIQUID RADWASTE EFFLUENT RADIATION LINE MONITOR Dil - N007 The liquid radwaste affluent line monitor provides alarm and automatic termination of release functions prior to exceeding the concentration limits specified in 107R 20, Appendix B, Table II, Column 2 at the release point to the unrestricted area.

To meet this specification, the alam/ trip setpoints l

for the liquid effluent monitor and flow measurement devices are set to assure j

that the following equation is satisfied p

y$Cypg i

l l

0004, Femi-2

1. 0-1 274W/0051W, 05/07/84

-o the effluent concentration limit (Specific: tion 3.11.1.1) implementing 10CFR 20 for the site, corresponding to the specific

- mix of radionuclides in the effluent stream being considered for dischstge, in y Ci Anl.

f a

= the setpoint, in pCi/m1, of the radioactivity monitor measuring 5

the radioactivity concentration in the effluent line prior to dilution and subsequent release; the setpoint, which is inversely phiportional to the volumetric flow of the effluent line and pro-portions 1 to the volumetric flow of the dilution stream plus the effluent stream, represents a value which, if exceeded, would i

result in concentrations er.ceeding the limits of 100FR 20 in the unrestricted area.

f

= the flow setpoint as determined at the radiation monitor location,

)

in volume per unit time, but in the same units as F, below.

I 1

(

i F

= the dilution water flow setpoint as determined prior to the release I

I point, in volume per unit time.

f t

l At Fermi-2, the Liquid Radoeste System Weste Sample Tanks discharge to the 1

Circulating Water Reservoir Decant Line to Lake Erie.

This decent line

(

)

furnishes the dilution flow (F).

The waste effluent flow (f) and the monitor f

setpoint (c) for the liquid redweste pathway are determined and set to meet I

l the conditions of the equation for a given effluent concentration' MC' f

{

The method by which this is accomplished is as follows:

l I

Step 1) The radionuclide concentration for a vaste sample tank to be released

[

is obtained from the sum of measured concentrations as determined by i

j the analyses required in STS Table 4.11-1:

f

{C1 =[ Cg + ( C, + C, + Cf+C) f g

9 iftere 1

l C,

a the concentration, C, of om mesuM p Wtter erW W

[

g genene-ray spectroscopy of each weste sample.

i 0D00, Fe mi-2 1.0-2 i

27de/0D$1W, OS/07/84 L

I

-I I

f C

'a the concentration of alpha emitters in liquid tasto as g

measured in the MONTH.Y composite sample.

(NOTE:

Sample is analyzed for gross a).

C,

= the measured concentrations of Sr-89 and Sr-90 in liquid waste as observed in the QUARTERLY composite sample.

C

= The measured concentrations of Fe-55 in liquid waste as observed in 7

the QUARTERLY composite sample.

i-C

= the measured concentration of H-3 in liquid waste as determined t

from analysis of the MONTH.Y composite sample.

The C term will be included in the analysis of each batch; terms for alpha, g

strontiums, iron, and tritium may be included as appropriate.

Step 2) The measured radionuclide concentrations are used to calculate a Dilution Factor, DF, which is the ratio of total' dilution flow rate to tank flow rate required to assure that the limiting concentrations of 107R 20, Appendix B, Table II, Column 2 are met at the point of discharge.

DF =

1

+ SF E

i

[ _C1.+p[MPC C \\ + SF C

C C

a s

f t

=

+

+

+

,g MPC MPC g

a s

MPCr MP where C

= measured concentrations of C,

C,,

b, C

and C

as y

g s

7 t

defined in Step 1.

Terms C,,

C, C,

and C

will be s

7 t

included in the calculation as appropriate.

l OD(N, Fermi-2

1. 0-3 2766W/0051W, 05/07/84

F.

MPC a MPC,

MPC,,

MPC,

MPC,

and MPQ cre limiting cone ntra-f g

s 7

tions of the appropriate radionuclide from 10CFR 20, Appendix B, Table II, Column 2.

For dissolved or entrained noble gases, the

~

concentration shall be limited to 2

x 10 pCi/ml total activity.

SF

= the safety factor; a conservative factor used to compensate for statistical fluctuations and errors of measurements.

(For example, SF = 0.5 corresponds to a 100 percent variation.)

Step 3) The dilution flow rate setpoint for minimum dilution flow rate, F '

d is established at ninety percent of the expected dilution flow rate:

(0.9) x (Circulating Water Reservoir F

=

d Decant Line Flow Rate )

Step 4) For the case DF < 1, the waste sample tank effluent concentration meets the limits of 107R 20 without dilution and effluent discharge flow rate may be assigned any desired value.

For DF >

1, the maximum permissible discharge flow rate, f, must be calculated:

t d+Ip :

d for F " I ft=

d 9

W W

where:

F

= Dilution flow rate to be used in effluent monitor setpoint d

calculations.

F

= (0.9) x (Circulating Water Reservoir Decant Line Flow Rate) d DF

= Dilution Factor from step 2.

f

= Flow rate of Waste Sample Tank discharge.

(This value will have an p

upper limit of the maximtn discharge capacity of the particular waste sample tank ptmp.)

ODCN, Fermi-2 1.M 2766W/0051W, 05/07/84 j

-\\

NOTE: If radioactivity from plant operations accumulatts in the Circulat-ing Watsr Reservoir such that measurablo quantitics of radio-nuclides are detected in the Circulating Water Reservoir, calcula-i tion of F must include a term to account for radioactivity d

present in the dilution stream prior to the introduction of the l

waste sample tank effluent:

F

= (Circulating Water Reservoir Decant Line Flow Rate) x (0.9) x (1 -

d APS fraction of Circulating Water Reservoir).

Step 5) The liquid radwaste effluent radiation monitor setpoint may now be determined based on the values of I C, ft and Fd whicn were 1

i specified to provide compliance with the limits of 10CFR 20, Appendix B, Table II, Column 2.

The monitor response is primarily to gamma The radiation,therefore,theactualsetpointisbasedongC.

g monitor setpoint which corresponds to the particular setpoint concentration, c, is determined based on monitor calibration data or on operational data which correlates monitor response to sample analyses associated with actual effluent releases.

(Example of monitor calibration graph is shown in Figure 1.0-1.)

The setpoint concentration, c, is determined as follows:

c = A [ C P.C.1, g

g ml where A

= Adjustment factor which will allow the setpoint to be established in a practical manner for convenience and to prevent spurious alarms.

1 I

ft (See Note 2 below)

=

f(actual)

If A > 1, Calculate c and determine the naximum value for the actual monitor setpoint (pCi/ml).

If A < 1, No release may be made. Re-evaluate Steps 2, 3, and 4.

0004, Fermi-2 1.05 2766W/0051W, 05/07/84 l

NOTE 1: The calculated cotpoint concentration, c, establishes the base value for the monitor s;tpoint.

How v;r, in cstablishing the actual monitor setpoint for a particular monitor, background radiation levels must be considered.

Normally, the actual monitor setpoint includes the calculated setpoint value plus background.

Background levels must be controlled such that radioactivity levels in the effluent stream being monitored can be accurately assessed at or below the calculated setpoint value.

NOTE 2: If DF < 1, A = (1/DF)

If calculated setpoint values are near actual concentrations planned for release, it may be impractical to set the monitor alarm based on this value.

In this case a new setpoint may be calculated by decreasing the effluent flow, increasing the dilution flow, or by decreasing { Ci by further processing of the liquid radwaste planned for release, and by following the methodology presented in Steps 2, 3, and 4.

Within the limits of the conditions stated above, the monitor setpoint for the Liquid Radwaste Effluent Radiation Monitor is determined as follows:

Liquid Radwaste Effluent Radiation Monitor D11 - N007 Perform Step 2), solving the equation for DF using the appropriate values in the concentration term from the sample analyses for the Liquid Radwaste Sample Tank batch to be discharged. Then perform Steps 3), 4), and 5) to determine the monitor setpoint.

If no discharge is planned for this pathway, the monitor Mtpoint should be established as close to background as practical to prevent spurious alarms and yet alarm should an inadvertent release occur.

1.1.2 CIRCULATING WATER RESERVOIR DECANT LINE RADIATION MONITOR D11 - N402 The Circulating Water Reservoir Decant Line is the blowdown line to Lake Erie, and it furnishes dilution for liquid radwaste discharges.

The radiation ODCM, Fermi-2 1.0-6 2766W/0051W, 05/07/84

~...

~.

_._.. - -...-...- ~. - _

y monit r haa no control function, but serv;s as support (backup) for the Liquid Radwaste Effluent Line Monitor.

The radiation monitor setpoint is established as follows:

c=([C)+ DF g

9 where I C and DF have values as determined in Section 1.1.1 Step 1 and g

9 Step2 respectively for the liquid radwaste sample tank planned for release.

(For practicality, for this monitor only, if DF is determined to be < 1, DF l

may be set equal to 1 for the purpose of calculating the monitor setpoint.)

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ti.; i; jo-3 5 6 10 1o 10 10 10 CPM

1.2 - DOSE CALO1ATION FOR LIQUID EFFLUENTS For liquid dose calculations consideration is given to the two primary current of Lake Erie. The flow patterns existing in the Lagoona Beach embayment maximum potential individual exposure is expected to exist with the current flow in, the northerly direction and only the fish consumption pathway "f considered in the liquid dose calculations. However, in the case when the current flow is in the southerly direction, the nearby location of the municipal water 1..take for the city of Monroe makes it desirable to consider I the water consumption pathway as well as the fish consumption pathway. The methodology for both cases is described in the following sections. 1.2.1 DOSE TO mITICAL RECEPTOR DUE TO FISH CONSt.NPTION The dose contribution to the maximum exposed individual by way of fish consumption from all radionuclides identified in liquid effluents released to unrestricted areas is calculated using the following expression: m -A ticF = A M C e DT gT g yg g 1 where D = The ctsnulative dose commitment to the total body or any organ, T, due to radioactivity in liquid effluents for the total time period m I A tg, in mrem (Reference 1). i =1 and At = The length of the Ath time period over which Cg g F are averaged for all liquid releases, in hours. g = The average concentration of radionuclide, i, in undiluted liquid C3 effluent during time period At from any liquid release, in g yC1/ml. i = The decay constant for radio.iuclide 1. (sec.1) ~ l y i 1.0-9 ODCM, Fe11ni-2 2766W/0051W, 05/07/84 i

t = The transit time -to the location of the individual cxpectcd to c receive the greatest potential dose due to the liquid pathway (1770m northeast of Fermi-2); 13,000 seconds. (Reference 5 Section 2.4.12). kW aw IWd F = 'Ihe near field average dilution factor for c 13 g Defined as the ratio of the undiluted liquid ,,ffluent release. e waste flow during release to the product of the average flow fran the discharge structure to unrestricted receiving water times Z. (average undiluted liquid waste flow) Fg = laverage T10w from the discharge structure during periods of radioactive materials release) x (Z) NOTE: The denominator is limited to 1000 cfs or less. (Reference 1, Section 4.3). where Z = Applicable dilution factor for the receiving water body at Fermi-2. Z = 10 (Reference 1, Section 4.3; Reference 5, chapter 5, Section 5.2.) A = The site related fish ingestion dose commitment factor to the total g body or any organ T for each identified principal gamma and beta emitter listed in Table 1.2-3 in mrem /hr per pCi/ml. Ah=K (4 BF ) 0Ff f where 5 K, = units conversion factor 1.14 x 10 1 l 6 10 x 10 m + 8760 = Adult fish consumption (21 kg/yr). 0004, Fermi-2 1.0-10 2766W/0051W, 05/24/84

BF a Bioacetsnulation fccter for rtdionuclide i, in fish, in pCi/kg par g pCi/1 from Table 1.2-1 (taken from Reference 3, Table A-1). DF = Dose conversion factor for radionuclide i, for adults in g preselected organ, t, in mrem /pCi, from Table 1.2-2 (taken from Reference 3, Table E-11). If radioact'$vity in the Circulating Water Reservoir Decant Line becomes > l LLD, prior to the junction with the Liquid Radwaste Effluent Line, that j concentration must be included in the dose determination. For this part of the dose calculation, F = 1 and At = the entire time period for which g the dose is being calculated. 1.2.2 DOSE DUE TO FISH AND DRIfEING WATER CONSlNPTION The dose contribution to an exposed individual by way of fish and drinking water consumption from all radionuclides identified in liquid effluents released to unrestricted areas is calculated using the following expression: m At m At g g b AR' 1 ST bNAR* U T" it g,1 g,y where i D = The ctsnulative dose commitment to the total body or any organ, T, due to radioactivity in liquid effluents for the total time period m I At, in mrem (Reference 1). g A =1 At = The length of the Ath time period over which Cg and g F are averaged for all liquid releases, in hours. g C = The average concentration of radionuclide, i, in undiluted liquid g effluent during time period At from any liquid release, in g yCi/ml. 0004, Fermi-2 1.0-11 ~ 2766W/0051W, 05/07/84

A = The decay constar" for radionuclide 1. (sec.~1) g t~ = The transit time to the location 153On south of Fermi 2; 11,000 g sgonds. (Reference 5, Section 2.4.12) t = The transit time to the city of Monroe water intake; 23,000 d seconds. (Reference 5, Section 2.4.12) F 'Ibe near field average dilution factor, for c during any liquid = g effluent release. Defined as the ratio of the undiluted liquid waste flow during release to the product of the average flow fran the discharge structure to unrestricted receiving water times Z. (average undiluted liquid waste flow) Fg = (average flow from the discharge structure during periods of radioactive materials release) x (Z ) NOTE: The denominator is limited to 1000 cfs or less. (Reference 1, Section 4.3). where Z = Applicable dilution factor for the receiving water body at Fermi 2. 10 (Reference 1, Section 4.3; Reference 5, Chapter 5 Section 5.2.) = ODCM, Fermi-2 1.0-12 2766W/0051W, 05/24/84

A'y = The site related drinking water ingestion dose commitment factor to the total body or any organ T for each identified principal gamma and beta emitter listed in Table 1.2-4 in mrem /hr per pCi/ml. A'ir = K,( ) DFy where = Units conversion factor 1.14 x 10' Kg 6 3 10 Ci x 10 ml + 8760 hr T 5 V 4 = Adult water consumption (730 liters / year). Dy = Dilution factor from the near field within one-quarter mile of the release point to the potable water intake for adult water consunption for Fermi 2 Plant, g = 7.7 tReference 5, Chapter 5, Section 5.3) DF = Dose conversion factor for nuclide i, for adults in preselected y organ, T, in m::em/pC1, from Table 1.2-2 (taken from Reference 3, Table E-11). A = Sea Section 1.2.1 h If radioactivity in the Circulating Water Reservoir Decant Line becomes > LLD, prior to the junction with the Liquid Radwaste Effluent Line, that concentration must be included in the dose determination. For this part of 1/Z, and A t = the entire time period the dose calculation, F = g for which the dose is being calculated. I 1 0D04, Fermi-2 1.0-13 2766W/0051W, 05/24/84 t

TTaLE 1.2-1 l BI0 ACCUMULATION FACTORS (pCi/kg per pCi/litsr)* FRESHWATER ELEENT FISH i H 9.E-01 C 4.6E 03 NA 1.0E 02 P 1.0E 05 CR 2.E 02 M. NN 4.0E 02 FE 1.0E 02 CO 5.0E 01 NI 1.E 02 CU 5.0E 01 ZN 2.E 03 I BR 4.2E 02 RB 2.0E 03 SR 3.0E 01 Y 2.5E 01 ZR 3.3E 00 NB 3.E 04 MO 1.0E 01 TC 1.5E 01 RU l.0E 01 RH 1.0E 01 AG 2.3E 00 TE 4.E 02 I 1.5E 01 CS 2.E 03 BA 4.0E 00 LA 2.5E 01 CE 1.0E 00 l PR 2.5E 01 NO 2.5E 01 W 1.2E 03 l NP 1.0E 01 ' Values in Table 1.2-1 are taken from Reference 3, Table A-1. f 0004, Fermi-2 1.0-14 2766W/0051W, 05/07/84 i

TABLE 1.2-2 Pagm 1 of 2 ADULT INGESTION DOSE FACTORS * ) (mrem /pCi ingested) COME L Ivf 4 f.80CY TNve080 EIONEY EUNC df-LLI hvCLII;E M 3 NO 04fa 1.35E-07 1.CSE-07 8.GSE-07 1.05E-07 4 0$E-07 1.05E-07 C 14.. 2.84E-06 5.68E-07 5.68E-07 5.68E-47 5.68E-07 5.68E.07 5.68E-07 Na 24..t.70E-06 1.70E-06 1.70E-06 f.F0E-06 1 70E-06 1.70E.06 1.70E-06

  1. 32 1.93E-04 1.20E-05
7. 4 6E-0 6 NO Data NC Data 40 cara 2.17E-05 CR St NO Data 90 CaTa 2.66E-09 1.59E-09 5 86E-10 3.53E.09 6.69E.07 NN 54 NO Cafa 4.57E.06 8.72E-OF NO Cata I.36E-06 NO DATA 1 40E-05 NN 56 NO Cafa 1.15E-07 2.04E-08 NO Data I.46E-07 NO Data 3 67E-06 ft 55 2.75E-06 1.90F-06 4.4AE-07 NO Cafa NO Data 1.06E-06 1.09E-06
  1. E 59 4.34E-06 t.02E-05
3. 9 t E-0 6 NO Data NO Data 2 85E-06 3.60E-05 CO 58 NO Cata 7.456-07
8. 6 ? E-0 6 NO Dafa ND 04T4 Nb caTA 1.5tE-05 CO to NO Data 2.14F-06 4.72E-06 NO 0474 No Data NO Dafa 6.02E-05 NI 63 1.30E-C4 9.0tf-06 4.36E-06 40 Data NO DATA NO 04fa 1.88E-06 NI 65 5.28E-07 6.86E-08 3.13 E -0 8 NO Oara NO Da TA NO Data 1.74E-06 i

Cu 66 NO Data 8.33E-08 3.9 t E-0 8 NO DATA 2 30E-07 NO Dafa 7.10E-06 2N 65 4.84E-06 1.54E-05

6. 9 e E -0 6 NO cara 1.03E-05 NO Cata 9.70E-06 EN 69 1.03E-08 t.47E-08
1. 3 7 E-0 9 NO Cafa 1.28E-08 NO cara 2.96E-09 pa e3 No cafa NO Cafa
4. 02 E-O n NO Dafa No caTA NO Data 5.79E-08 88 84 NO Dafa NO Data 5.2tE-08 NO Data 40 DATA NO Dafa 4.09E-13 SR 85 NO Caf a 40 DATA 2.14 E-0 9 40 Data NO DATA NO DATA L7 E-24 48 86 NO Data 2.ttE-05 9.83E-06 No DATA

=0 DATA No DATA 4.16E-06 28 88 NO Data 6.051-08 1.21E-08 NO DATA NO caTa 40 Dafa 8.36E-19 48 89 NO Data 4.01E-08 2 82E-08 NO DATA NO DATA NO Cafa 2.33E SR 89 3.08E-04 =0 Data 8.84E-06 No cara No Cara no Oafa 4.94E-05 58 90 7.58E-03 NO Data 1.86E-03 40 Data No caTA NO Data 2.19E-04 Sm 91 5.67E-06 NO Data 2.29E-07 No cafa NC Dafa NO Cata 2 70E-05 5a 92 2.15E-06 NO Data 9 30E-08 NO Data NO DATA No cafa 4.26E-05 l T 90 9.62E-09 NO Data 2 58E-10 NO DATA NO Data NO 06TA 1.02E-04 t 9tN 9.09E-It NO Data 3.52E-12 NO Dafa NO Dara NO Data 2.67E-10 i Y 91 1.4 t E-0.7 NO Data 3.77E-09 NO Cafa NO OaTA No para 7.76E-05 V 92 8.45E-10 NO Cafa 2.47E-11 NO Cara NO DAT4 NO Da7a 1.48E-05 v 93 2.68E-C9 No cara 7.40E-It NO Dafa NO Data NO Data 8.50E-05" 24 95 3.0*E-08 9.75E-09

6. 6 0 E-0 9 NO DATA 1.53E-08 NO Cafa 3.09E-05 la 97 1.68E-09 1.39E-10 1.55E-to NO Data 5.12E-to No cara I.05E-06 M4 95 6.22E-09 3.66E-09
8. 86E-0 9 NO Data 3.42E-09 NO Dara 2.10E-05 i

i j ~ NO Data 4.3tE-06 8.20E-07 No cara 9.76E-06 NO Data 9.99E-06 TC 99a 2.47E-lo 6.98!-10 8 89E-09 NO Dafa 1.06E-08 3.42E-10 4.13E-07 NO 99 t TC101 2.54E-10 3.66E-to 3.59E-09 NO Data 6.59E-09 1.87E-10 t.80E-28 tut 03 4 85E-07 NO Cafa 7.9 f f =0 8 =0 Data T. 06E-O F NO 04Ta 2.16E-05 1.54E.08 Nu Daf.

6. 0 8 E.0 9 No Car.

1.99E.Or NO Dara 9.62E-Os autos i i ' Values in Table 1.2-2 are taken from Reference 3, Table E-11. i 1.0-15 ODCN, Fermi-2 2766W/0051W, 05/07/84 1

TABLE 1.2-2 (Continued) Page 2 of 2 1 1 1 l i l apuCL 4 Of SONE LIvga f.600f tava01C EIONEf LUNG Gt-LLI Rut 06. 2.FSE-06 NO Oafa

3. 4 e E-0 7 No cara 5.3tE-06 N0 cara 1.7st.04 aGi l o m*

1.60E-07 t.40E-07 8.79E-08 No Data 2 9tE.07 No Data 6.06E-05 4 FEt25m 2.69E-06 9.7tE-07

3. 51E-0 7 0.06E-07 1.09E-05 NO Data 1.07E-05 TEt27*

6.77E-06 2.42C-06

8. 2 5E -0 7 8.73E-06 2.75E-05 NO Oata 2.27E-05 i

FE127 1.10E-0F 3 95E-OS 2 38E-Os 8.tSE-00 4.4eE-07 NO Data 8.68E-06 TE129N 1.15E-05 4.29E-06 1.A2E-06 3.95E-06 4.80E-05 NO Cafa 5.79E-05 TEt29 3.16E-08 1 18E-Os 7.63E-09 2 4tE-08 1 32E-07 No cafa 2.37E-08 TEt3tm 1.73E.06 3.46E.07

7. 0 5 E -0 7 t.36E-06 a.57E-06 No Data s.40E.05 TE138 1.97E-08 8 23E-c9
6. 22 E -0 9 1 62E-08 9.63E-08 NO Cara 2.79E-09

+ 8E132 2.52E-06 1 6 3E-06 1.5JE-06 1 80E-06 1.57E-Qj No cara 1.7tE-05 t 130 7.56E-07 2.23E-06

0. 4 0 E -0 7 1 89E-06 3 48E-06 NO Data I.92E-06 I 131 4.86E-06 5 95E-06
3. 4 t E-0 6 1.95E-03 1 02E-o? No Oara 1.57E-06 I 132 2.03E-07 5.43E-07 1.90E-07 t.90E-05 8.65E-07 NO Cafa 1.02E-07 l

1 133 1 42E-06 2.4FE-06 7.53E-07 3 63E.04 4.3tE-06 No caTa 2.22E-06 j i 136 1.06E-07 2.80E-07 1.03E-0 F 4.99E-06 4.5eE-07 NO DATA 2.5tf-10 j I 135 4.43E-07 1.16E-06 4.2SE-07 7.65E-05 1.86E-06 No Data 1.31E-06 C5:36 6.22E-05 1.48E-04 B.21E-04 NO Cata 6.79E-05. 1 59E-05 2.59E-06 CSI16 6.5tE-06 2.57E-05 1.e5E-05 NO Oafa 1.43E-05 1 96E-06 2.92E-06 4 i C5137 7.97E-05 1.09E-06 7.14 E -0 5 No Data 3.70E-05 1 23E-05 2.IIE-06 C5138 5.52E-0s 3.c9E-07 5.40E-Os No cafa s.01E-08 7.9tE-09 4.65E-13 sat 39 9.70E-00 6.9tE-Il

2. 8 4 E -0 9 NO Data 6.66E-11 3.92E-11 1.72E-07

...........v=-- sal 60 2.03C-05 2.55E-00 1.33E-06 N0 nata s.ntt.09 1.46E-08 4.18E-05 f Ralst 4.?tE-08 1.56E-11 1.59E-09 40 Data 3.3tE-It 2.02E-11 2.22E-17 tats? 2.13E.08 2.19E-II

1. 3 6 E -0 9 NO Cata 1.35E-It t.24E-11 1.00E-26 Lat*C 2.30E-09 1.26E-09 J.3JC-10 NU Data NO Cafa NO Dafa 9.25E-05 Lat*2 1.28E-10 5.82E-11 I.45E-11 NO Data NO Cata NO Cara 4.25E-07 CEt*l 9.36E-09 6.J3E-09 F. t et-t o NO Dafa 2.94E-09 NO Cafa 2.42E-05

} CE163 1.65E-09 1.22E-06 1.35E-10 NO DATA 5.37E-10 NO Cata 4.56E-05 4 l CE t*6 4.aeE-07 2.04E-07 2.62E-08 NO Cafa 1.2tE-07 NO Data 1.65E-06 page3 g.20E-09 3.69E.09 6 56E-to No Data 2.13 E -09 NO Cata 4.03E-05 l i, pat 44 3.01E-II 1.25E-tt 1.5 sE-12 NO Cata 7.0$E-12 No DaT A - 4.33E-te N0l67 6.29E-09 7.27E-09 4.35E-10 NO DAfa 6.25E-09 NO Data 3.69E-05 N 897 1.03E-07 8.6tE-08 3.01E-Os NO Data NO Oata No CaTa 2.82E-05 Nr239 1.19E-09 1.17C-10 6.45E-1 i NO Data 3.65E-to NO Data 2 40E-05 l 1 1 i ' Values in Table 1.2-2 are taken from Reference 3, Table E-11. 0D04, Femi-2 1.0-16 i 2766W/0051W, 05/07/84 y.m,---7--a- - + - - - ,,y~wg--.3 --m m. r-- -. - ------g.- - - *--- +-----e r- ' - - * - * -e-r*ew-w -w w W---wee up-w w v-'e w -w e-

TABUE 1.2-3 Page 1 of 2 SITE RELATED INGESTION DOSE COMMITMENT FACTOR, Ait (FISH CO'NSLNPTION) (crem/hr per pCiAnl) NUCL1DE - BONE L1VER T. BODY THYRO 1D KIDHEY LUNG GI-LLI H-3 0.00E+00 2.26E-01 2.26E-01 2.26E-01 2.26E-01 2.26E-01 2.26E-01 C-14 3.13E+04 6.26E+03 6,26E+03 6.26E+03 6.26E+03 6.26E+03 6.26E+00 tia-24 4.07E+02 4.07E+02 4.07E+02 4.07E+02 4.07E+02 4.07E+02 4.07E+02 P-32 4.62E+07 2.87E+06 1.79E+06 0.00E+00 0.00E+00 0.00E+00 5.19E+06 Cr-51 0.00E+00 0.00E+00 1.27E+00 7.61E-01 2.81E-01 1.69E+00 3.20E+02 Mn-54 0.00E+00 4.38E+03 8.35E+02 0.00E+00 1.30E+03 0.00E+00 1.34E+0c Mn-56 0.00E+00 1.10E+02 1.95E+01 0.00E+00 1.40E+02 0.00E+00 3.51E+03 Fe-55 6.5SE+02 4.55E+02 1.06E+02 0.00E+00 0.00E+00 2.54E+02 2.61E+02 Fe-59 1.04E+03 2.44E+03 9.36E+02 0.00E+00 0.00E+00 6.82E+02 8.14E+03 Co-58 0.00E+00 8.92E+01 2.00E+02 0.00E+00 0.00E+00 0.00E+00 1.81E+00 Co-60 0.00E+00 2.56E+02 5.65E+02 0.00E+00 0.00E+00 0.00E+00 4.81E+00 tJi-63 3.11E+04 2.16E+03 1.04E+03 0.00E+00 0.00E+00 0.00E+00 4.50E+02 Ifi-65 1.26E+02 1.64E+01 7.49E+00 0.00E+00 0.00E+00 0.00E+00 4.17E+02 Cu-64 0.00E+00 9.97E+00 4.68E+00 0.00E+00 2.51E+01 0.00E+00 8.50E+02 In-65 2.32E+04 7.37E+04 3.33E+04 0.00E+00 4.93E+04 0.00E+00 4.64E+0c Zn-69 4.93E+01 9.43E+01 6.56E+00 0.00E+00 6.13E+01 0.00E+00 1.42E+01 Fr-83 0.00E+00 0.00E+00 4.04E+01 0.00E+00 0.00E+00 0.00E+00 5.82E+01 Er-84 0.00E+00 0.00E+00 5.24E+01 0.00E+00 0.00E+00 0.00E+00 4.11E-Oc fr-85 0.00E+00 0.00E+00 2.15E+00 0.00E+00 0.00E+00 0.00E+00 1.01E-15 Fb-86 0.00E+00 1.01E+05 4.71E+04 0.00E+00 0.00E+00 0.00E+00 1.99E+0c Fb-88 0.00E+00 2.90E+02 1.54E+02 0.00E+00 0.00E+00 0.00E+00 4.00E-09 Fb-89 0.00E+00 1.92E+02 1.35E+02 0.00E+00 0.00E+00 0.00E+00 1.12E-11 Sr-89 2.21E+04 0.00E+00 6.35E+02 0.00E+00 0.00E+00 0.00E+00 3.55E+03 Sr-90 5.44E+05 0.00E+00 1.34E+05 0.00E+00 0.00E+00 0.00E+00 1.57E+0c tr-91 4.07E+02 0.00E+00 1.A4E+01 0.00E+00 0.00E+00 0.00E+00 1.94E+00 Sr-92 1.54E+02 0.00E+00' 6.68E+00 0.00E+00 0.00E+00 0.00E+00 3.06E+00 Y-90 5.76E-01 0.00E+00 1.54E-02 0.00E+00 0.00E+00 0.00E+00 6.10E+00 Y-91n. 5.44E-03 0.00E+00 2.11E-04 0.00E+00 0.00E+00 0.00E+00 1.60E-02 T-91 8.44E+00 0.00E+00 2.26E-01 0.00E+00 0.00E+00 0.00E+00 4.64E+0:' Y-92 5.06E-02 0.00E+00 1.4SE-03 0.00E+00 0.00E+00 0.00E+00 8.86E+02 4-93 1.60E-01 0.00E+00 4.43E-03 0.00E+00 0.00E+00 0.00E+00 5.09E+0:. Cr-95 2.40E-01 7.70E-02 5.21E-02 0.00E+00 1.21E-01 0.00E+00 2.44E+02 2r-97 1.35E-02 2.68E-03 1.22E-03 0.00E+00 4.04E-03 0.00E+00 8.30E+02 t'b-95 4.47E+02 2.4BE+02 1.34E+02 0.00E+00 2.46E+02 0.00E+00 1.51E+06 Mo-99 0.00E+00 1.03E+02 1.96E+01 0.00E+00 2.34E+02 0.00E+00 2.39E+02 Tc-9?ni 8.87E-03 2.51E-02 3.19E-01 0.00E+00 3.81E-01 1.23E-02 1.48E+0! Ic-101 9.12E-03 1.31E-02 1.29E-01 0.00E+00 2.37E-01 6.72E-03 3.95E-lo Fu-103 4.43E+00 0.00E+00 1.91E+00 0.00E+00 1.69E+01 0.00E+00 5.17E+02 Fu-105 3.69E-01 0.00E+00 1.4SE-01 0.00E+00 4.76E+00 0.00E+00 2.26E+02 ODfN, Fermi-2 REV.0 1.0-17 2766W/0051W, 01/31/83

l 1 TABLE 1.2-3 (Continued) Page 2 of 2 NUCLIDE SONE LIVER T.30DY THYROID KIDNEY LUNG GI-LLI Ru-106 6.58E+01 0.00E+00 8.33E+00 0.00E+00 1.27E+02 0.00E+00 4.26E+03 Rg-110m 8.01E-01 8.15E-01 4.84E-01 0.00E+00 1.60E+00 0.00E+0'8 3.33E+02 Te-125m 2.57E+03 9.30E+02 3.44E+02 7.72E+02 1.04E+04 0.00E+00 1.02E+0c Te-127m 6.48E+03 2.32E+03 7.90E+02 1.66E+03 2.63E+04 0.00E+00 2.17 E + 0 4-Te-127 1.05E+02 3.78E+01 2.28E+01 7.80E+01 4.29E+02 0.00E+00 8.31E+03 i Te-129m 1: 10E+04 4.11E+03 1.74E+03 3.78E+03 4.60E+04 0.00E+00 5.54E+0c Te-129 3.01E+01 1.13E+01 7.33E+00 2.31E+01 1.26E+02 0.00E+00 2.27E+0! Te-131m 1.66E+03 0.10E+02 6.75E+02 1.28E+03 8.21E+03 0.00E+00 8.04E+0c Te-131 1.89E+01 7.08E+00 5.96E+00 1.55E+01 8.26E+01 0.00E+00 2.67E+00 Te-132 2.41E+03 1.56E+03 1.47E+03 1.72E+03 1.50E+04 0.00E+00 7.38E+0c I-130 2.71E+01 8.01E+01 3.16E+01 6.79E+03 1.25E+02 0.00E+00 6.89E+01 1-131 1.49E+02 2.14E+02 1.22E+02 7.00E+04 3.66E+02 0.00E+00 5.64E+01 1-132 7.29E+00 1.95E+01 6.82E+00 6.82E+02 3.11E+01 0.00E+00 3.66E+00 1-133 5.10E+01 8.87E+01 2.70E+01 1.30E+04 1.55E+02 0.00E+00 7.97E+01 I-134 3.81E+00 1.03E+01 3.70E+00 1.79E+02 1.64E+01 0.00E+00 9.01E-03 1-135 1.59E+01 4.17E+01 1.54E+01 2.75E+03 6.68E+01 0.00E+00 4.70E+01 Cs-134 2.98E+05 7.09E+05 5.79E+05 0.00E+00 2.29E+05 7.61E+04

1. 2 4 E + 0 4-Cs-136 3.12E+04 1.23E+05 8.86E+04 0.00E+00 6.85E'04 9.38E+03 1.40E+0c Cs-137 3.82E+05 5.22E+05 3.42E+05 0.00E+00 1.77E+05 5.89E+04 1.01E+0c Cs-138 2.64E+02 5.22E+02 2.59E+02 0.00E+00 3.84E+02 3.79E+01 2.23E-03 Ea-139 9.29E-01 6.62E-04 2.72E-02 0.00E+00 6.19E-04 3.75E-04 1.65E+00 Ea-140 1.94E+02 2.44E-01 1.27E+01 0.00E+00 8.30E-02 1.40E-01 4.00E+02 i

Ea-141 4.51E-01 3.41E-04 1.52E-02 0.00E+00 3.17E-04 1.93E-04 2.13E-10 Ba-142 2.04E-01 2.10E-04 1.28E-02 0.00E+00 1.77E-04 1.19E-04 2.87E-19 La-140 1.50E-01 7.54E-02 1.99E-02 0.00E+00 0.00E+00 0.00E+00 5.54E+03 La-142 7.66E-03 3.48E-03,8.68E-04 0.00E+00 0.00E+00 0.00E+00 2.54E+01 i Ce-141 2.24E-02 1.52E 1.72E-03 0.00E+00 7.04E-03 0.00E+00 5.79E+01 Ce-143 3.95E-03 2.92E+00 3.23E-04 0.00E+00 1.29E-03 0.00E+00 1.09E+02 Ce-144 1.17E+00 4.8BE-01 6.27E-02 0.00E+00 2.90E-01 0.00E+00 3.95E+02 Fr-143 5.51E-01 2.21E-01 2.73E-02 0.00E+00 1.27E-01 0.00E+00 2.41E+03 I Fr-144 1.80E-03 7.48E-04 9.16E-05 0.00E+00 4.22E-04 0.00E+00 2.59E-10 Nd-147 3.76E-01 4.35E-01 2.60E-02 0.00E+00 2.54E-01 0.00E+00 2.09E+03 W-187 2.96E+02 2.47E+02 8.65E+01 0.00E+00 0.00E+00 0.00E+00 8.10E+0c d Op-239 2.85E-02 2.80E-03 1.54E-03 0.00E+00 8.74E-03 0.00E+00 5.75E+02 i 5 OD W, Feini-2 REY.0 1.0-18 2766W/0051W, 01/31/83

TABLE 1.2-4 Page 1 of 2 SITE RELATED INGESTION DOSE COMITMENT FACTOR, A'h (WATER CONSLMPTION) (arem/hr per pCiA1) .. ~ NUCLIDE BCNE LIVER T. BODY 'INYROID KIENEY IUNG 1 GI-ILI H-3 0.00E+00 1.14E+00 1.14E+00 1.14E+00 1.14E+00 1.14E+00 1.14E+00 C-14 3.06E+01 6.14E+00 6.14E+00 6.14E+00 6.14E+00 6.14E+00 6.14E+00 l Na-24 1.83E+01 1.83E+01 1.83E+01 1.83E+01 1.83E+01 1.83E+01 1.83E401 P-32 2.09Ev03 1.30E+02 8.06E+01 0.00E+00 0.00E+00 0.00E+00 2.35E+02 Cr-51 0.00E+00 0.00E+00 2.87E-02 1.71E-02 6.34E-03 3.82E-02 7.23E+00 Mn-54 0.00E+00 4.94Et01 9.43E+00 0.00E+00 1.47E+01 0.00E+00 1.52E+02 Mn-56 0.00Ev00 1.24E+00 2.21E-01 0.00E+00 1.58Ev00 0.00E+00 3.96E+01 Fe-55 2.97Et01 2.05E+01 4.79E+00 0.00E+00 0.00E+00 1.15E+01 1.18E+01 Fe-59 4.69E+01 1.10E+02 4.22E+01 0.00E+00 0.00E+00 3.08E 01 3.68Et02 Co-58 0.00E+00 8.05E+00 1.81E+01 0.00E+00 0.00E+00 0.00E+00 1.64E+02 00-60 0.00E+00 2.31E+01 5.10E+01-0.00E+00 0.00E+00 0.00E+00 4.35E+02 l Ni-63 1.40E+03 9.74E+01 4.71E+01 0.00Ev00 0.00E+00 0.00E+00 2.03E+01 Ni-65 5.70E+00 7.42E-01 3.38E-01 0.00E+00 0.00E+00 0.00E+00 1.88E+01 Cu-64 0.00Et00 9.00E-01 4.22E-01 0.00E+00 2.27E+00 0.00E+00 7.6t}Ejg1 1 Zn-65 5.23E+01 1.66E+02 7.52E+01 0.00E+00 1.11E+02 0.00E+00 1.05E+02 Zn-69 1.11E-01 2.13E-01 1.46E-02 0.00E+00 1.39E-01 0.00E+00 3.19E-02 i Br-83 0.00Et00 0.00E+00 4.35E-01 0.00E+00 0.00E+00 0.00E+00 6.26E-01 i Br-84 0.00E+00 0.00E+00 5.64E-01 0.00E+00 0.00E 00 0.00E+00 4.42E-06 Br-85 0.00E+00 0.00E+00 2.31E-02 0.00E+00 0.00E+00 0.00E+00 1.08E-17 Rb-86 0.00E+00 2.29E+02 1.06E+02 0.00E+00 0.00E+00 0.00E+rJ 4.49E+01 Rb-88 _ 0.00E+00 6.53E-01 3.47E-01 0.00E+00 0.00E+00 0.00E 00 9.04E-12 4 Rb-89 0.00E+00 4.34E-01 3.05E-01 0.00E'+00 0.00E+00 0.00E+00 2.52E-14 Sr-89 3.32E+03 0.00E+00 9.56E+01 0.00E+00 0.00E+00 0.00E+00 5.34E+02 Sr-90 8.19E+04 0.00E+00 2.01E+04 0.00E+00 0.00E+00 0.00E+00 2.36E+03 Sr-91 6.13E+01 0.00E+00 2.48E+00 0.00E+00 0.00E+00 0.00E+00 2.92E+02 Sr-92 2.32E+03 0.00E+00 1.01E+00 0.00E+00 0.00E+00 0.00E+00 4.61E+02 Y-90 1.04E-01 0.00E+00 2.79E-03 0.00E'+00 0.00E+00 0.00E+00 1.10E+0? Y-91;n 9.82E-04 0.00E+00 3.81E-05 0.00E+00 0.00E+00 0.00E+00 2.88E-03 Y-91 1.52E+00 0.00E+00 4.08E-02 0.00E+00 0.00E+00 0.00E+00 8.39E102 Y-92 9.13E-03 0.00E+00 2.68E-04 0.00E+00 0.00E+00 0.00E+00 1.60E+02 Y-93 2.90E-02 0.00E+00 8.00E-04 0.00E+00 0.00E+00 0.00Et00 9.18E+02 gr-95 3.29E-01 1.05E-01 7.13E-02 0.00E+00 1.65E-01 0.00Et00 3.34Et02 i Er-97 1.82E-02 3.66E-03 1.68E-03 0.00E+00 5.53E-03 0.00E+00 1.14E+03 16-95 6.73E-02 3.74E-02 2.01E-02 0.00Et00 3.70E-02 0.00E+00 2.27E+02 Mo-99 0.00E+00 4.66E+01 8.86E+00 0.00E+00 1.05E+02 0.00E+00 1.08E+02 Tc-99 2.68E-03 7.55E-03 9.61E-02 0.00E+00 1.15E-01 3.70E-03 4.47E+00 i Tc-101 2.74E-03 3.96E-03 3.88E-02 0.00E+00 7.12E-02 2.03E-03 1.19E-14 t l l 0004, Fermi-2 REV.0 1.0-19 2766W/0051W, 01/31/83 i

TABLE 1.2-4 (Continued) Page 2 of 2 NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI Ru-103 2.00E+00 0.00E+00 8.61E-01_ 0.00E+00 7.64E+00 0.00E+00 2.34E+02 Ru-105 1.66E-01 0.00E+00 6.57E-02 0.00E+00 2.16E+00 0.00E+00 1.02E+02 Ru-106 2 97E+01 0.00E+00 3 77E+00 0.00E+00 5.74E+01 0.00E+00 1.92E+03 Ag-110m 1.73E+00 1.60E+0D 9.51E-01 0.00E+00 3 14E+00 0.00E+00 6.53E+02 Te-125m 2 90E+00 1.05E+01 3.88E+00 8.71E+00 1.18E+02 0.00E+00 1.16E+02 Te-127m 7 31E+01 2.61E+01 8.92E+00 1.87E+01 2.97E+02 0.00E+00 2.45E+02 Te-127 1.19E+00 4.27E-01 2.57E-01 8.81E-01 4.84E+00 0.00E+00 9.38E+01 Te-129m 1.24E+02 4.64E+01 1.96E+01 4.27E+01 5 18E+02 0.00E+00 6.26E+02 -Te-129 3 39E-01 1.28E-01 8.27E-02 2.61E-01 1.43E+00 0.00E,00 ?.56E-01 Te-131m 1.87E+01 9.14E+00 7.62E+00 1.45E+01 9.26E+01 0.00E+00 9.08E+02 Te-131 2.13E-01 8.90E-02 6.73E-01 1.75E-01 9.32E-01 0.00E+00 3 01E-02 Te-132 2.73E+01 1.77E+01 1.65E+01 1.95E+01 1.70E+02 0.00E+00 8.34E+02 I-130 8.17E+00 2.42E+01 9.51E+00 2.04E+03 3.77E+01 0.00E+00 2.08E+01 _I-131 4.49E+01 6.43E+01 3.69E+01 2.10E+04 1.10E+02 0.00E+00 1.70E+01 I-132 2.19E+00 5.87E+00 2.05E+00 2.05E+02 9 35E+00 0.00E+00 1.10E+00 I-133 1.53E+01 2.68E+01 8.14E+00 3 92E+03 4.66E+01 0.00E+00 2.40E+01 I-134 1.15E+00 3.12E+00 1.llE+00 5.39 E+01 4.95E+00 0.00E+00 2.71E-03 I-135 4.79E+00 1.25E+01 4.62E+00 8.27E+02 2.01E+01 0.00E+00 1.42E+01 Cs-134 6.73E+02 1.60E+03 1.31E+03 0.00E+00 5.18E+02 l 1.71E+02 2.81E+01 Cs-136 7.04E+01 2.78E+02 2.00E+02 0.00E+00 1.55E+02 l 2.12E+01 3 16E+01 Cs-137 8.61E+02 1.18E+03 7.71E+02 0.00E+00 4.00E+02 1.32E+02 2.29E+01 Cs-138 5.96E-01 1.18E+00 5.83E-01 0.00E+00 8.66E-01 8.55E-02 5.03E-06 Ba-139 1.05E+00 7.47E-04 3 06E-02 0.00E+00 6.99E-04 4.23E-04 1.86E+00 -Ba-140 2.19E+02 2.75E-01 1.44E+01 0.00E+00 9.38E-02 1.58E-01 4.52E+02 Ba-141 5.09E-01 3.84E-04 1.71E-02 0.00E+00 3.57E-04 2.18E-04 2.40E-10 Ba-142 2.30E-01 2.36E-04 1.45E-02 0.00E+00 2.00E-04 1.34E-04 3.25E-19 La-140 2.70E-02 1.36E-02 3.60E-03 0.00E+00 0.00E+00 0.00E+00 1.00E+03 La-142 1.39E-03 6.29E-04 1.57E-04 0.00E+00 0.00E+00 0.00E+00 4.60E+00 _Ce-141 1.01E-01 6.84E-02 7.77E-03 0.00E+00 3.18E-02 0.00E+00 2.61E+02 Ce-143 1.78E-02 1.32E+01 1.45E-03 0.00E+00 5.81E-03 0.00E+00 4.92E+02 Ce-144 5.27E+00 2.21E+00 2.83E-01 0.00E+00 1.31E+00 0.00E+00 1.78E+03 Pr-143 9.95E+02 3.99E-02 4.92E-03 0.00E+00 2.30E-02 0.00E+00 4.35E+02 Pr-144 3.25E-04 1.35E-04 1.65E-05 0.00E+00 7.62E-05 10.00E+00 4.68E-11 Nd-147 6.79E-02 7.86E-02 4.70E-03 0.00E+00 4.60E-02 10.00E+00 3 77E+02 W-187 1.llE+00 9.31E-01 3.25E-01 0.00E+00 0.00E+00 0.00E+00 l3.05E+02 Np-239 1.29E-02 1.26E-03 6.97E-04 0.00E+00 3.95E-03 0.00E+00 2.60E+02 l l i ODCM, Fermi-2 REV.0 1.0-20 2766W/0051W, 01/31/83 --,r -w m

METHODOLOGY FOR INDIVIDUAL LIQUID DOSE PRO ICTIONS (To Determine Necessity of Operating Liquid Radwaste Treatment System) 1.2.3 = The'NRC requires that dose projections be performed to indicate whether cumu-I lative doses over a thirty-one (31) day period are likely to exceed 25% of the ennual design objective dose limit adjusted to a thirty-one (31) day period. The,25% actuation levels of 0.06 mrem total body dose and 0.2 mrem organ d tion of g tere selected by NRC based on their cost-benefit analysis for opera When the thirty-one (31) day projected dose exceeds 0.06 radwaste systems. mrem to the total body or 0.2 mrem to any organ, operation of appropriate portions of the radwaste systems would be required. When the percent of the quarterly limits exceed 4% for the total body or any organ (i.e. the cumulative total body dose exceeds OA6 mrem and the cumu organ dose exceeds 0.2 mrem) determine the thirty-one (31) day dose proje as follows: tb(accumulated) x 3[ ~ ~~ D X tb(prj) ~" D (accumulated) o x 3f = D (prj) X o where elapsed = the cumulative total body dose for tne Dtb(accumulated) portion of the current quarter plus the release under consideration for the particular reactor unit. = the cumulative organ doses for the elapsed portion D (accurnulated) of the current quarter plus the release under o consideration for the particular reactor unit. = the number of days into the current quarter to the X nearest whole day. 1.0-21 ODCN, Fermi-2 2766W/0051W, 05/24/84

If cctivitica planned during the remainder of the 31-day ptriod are expected to contribute a significant dose and the determination can be reasonably made, this contribution should be included in the equations: ~ tb(accumulated) X 3/ + Danticipated tb(prj) X D (accumulated) x [3d o + D o(prj) X anticipated where = the anticipated total body or organ dose resulting Danticipated from anticipated operational occurrences which may occur in addition to routine releases over the thirty-one (31) day period. > 0.2 mrem, 0.06 mrem or if D (prj) If Dtb(prj) o the appropriate portions of the Liquid Radwaste Treatment System must be used to process liquid waste prior to release. l l 1.0-22 ODCN, Fermi-2 2766W/0051W, 05/24/84

1.3 DEFINITIONS OF LIQUID EFFLUENT TERMS Section of Initial Use Term Definition 1.1.1 adjustment factor applied to facilitate setting actual A = monitor setpoints. 1.2 j the site related ingestion dose commitment factor due A, = y to fish consumption to the total body or any organ T for each identified principal gamma and beta emitter listed in Table 1.2-3 in mrem-ml per hr-yCi. 4 1.2.2 the site related ingestion dose commitment factor due to A = h water consumption to the total body or any organ t for each identified principal gamma and beta emitter listed in Table 1.2-4 in mrem /hr per pCi/ml. 1.2.1 Bioaccumulation Factor for nuclide i, in fish, pCi/Kg per BF = y pCi/1, from Table 1.2-1. 1.1.1 the effluent concentration limit (Specification 3.11.1.1) hC = implementing 10CFR 20 for the site, in pCi/ml. 1.1.1 the effluent concentration of alpha emitting nuclides C, = observed by gross alpha analysis of the MONTit.Y composite sample. 1.1.1 The concentration of Fe-55 in liquid wastes as C = 7 observed in the QUARTERLY composite sample. 1.1.1 the effluent concentration of a gamma emitting nuclide, g, C = g observed by gamma-ray spectroscopy of the waste sample. 1.1.1 the concentration of nuclide i as determined by the C = y analysis of the waste sample. 1.0-23 00CM, Fermi-2 2766W/0051W, 05/24/84

= _.. S:ction of Initia1 Uso Term Definition C = the average concentration of radionuclide, i, in undiluted 1.2.1 g from any liquid liquid effluent during time period Atg release, in yCi/ml. C, = the concentration of Sr-89 or Sr-90 in liquid wastes 1.1.1 "a's determined by analysis of the QUARTERLY composite sample. C. = the measured concentration of H-3 in liquid waste 1.1.1 t as determined by analysis of the MONTH Y composite. = the setpoint of the radioactivity monitor measuring the 1.1.1 c radioactivity concentration in the effluent line prior t to dilution and subsequent release. DF = a dose conversion factor for nuclide, i, for adults in 1.2.1 y preselected organ, t, in mrem /pCi found in Table 1.2-2. D = the currulative dose commitment to the total body or any 1.2.1 organ,T, from the liquid effluents for the total time period. DF = the dilution factor, which is the ratio of the total 1.1.1 dilution flow rate to the effluent stream flow rate (s) required to assure that the limiting concentration of 10CFR, Part 20, Appendix B, Table II, Column 2 are met at the point of discharge. i F = the dilution water flow monitor setpoint as determined 1.1.1 prior to the release point, in volume per unit time. (General expression for equation on page 1.0-1.) F = the flow rate of the dilution stream used for setpoint 1.1.1 d calculations during the time of release, which is (0.9) x actual dilution flow. 0D04, Fermi-2 1.0-24 2766W/0051W, 05/24/84

Section of Term Definition Initial Use f = effluent flow rate 1.1.1 P f = the flow setpoint as determined for the radiation monitor 1.1.1 location. (General expression.) f = maximum permissible effluent flow rate 1.1.1 t during any 1.2.1 F = the near field average dilution factor for Cg g liquid effluent release. K, = 1.14 x 105, units conversion factor. 1.2.1 MPC

MPC, MPC,, MPC,, %, and %

1.1.1 y the limiting concentrations of the appropriate gamma emitting radionuclides, alpha emitting radionuclides, strontium, iron and tritium, respectively, from 10&R, Part 20, Appendix B, Table II, Column 2. SF = the safety factor, a conservative factor used to compen-1.1.1 sate for statistical fluctuations and errors of measure-ments. t, = ene transit time to tne city of Monroe water intaae; 1.2.2 23,000 seconds. (Reference 5 Section 2.4.12) 0004, Fermi-2 1.0-25 276diW/0051W, 05/07/84

S:ction of T:rm Definition Initial Usa t = The transit time to the location of the individual 1.2.1 expected to receive the greatest potential dose due to the liquid pathway; 13,000 seconds. (Reference 5 Section 2.4.12) t = The transit time to the location 153On south of Fermi 2; g 11,000 seconds. (Reference 5, Section 2.4.12) At = duration of release under consideration. 1.2.1 m = number of liquid releases. 1.2.1 U = 21 kg/yr, fish consumption (adult). 1.2.1 F 4 = adult water consunption, 7301/ year. 1.2.2 2 = Applicable dilution factor for the receiving water body at Fermi 2j 10 1 = The decay constant for radionuclide 1. (sec~1) 1.2.1 1 l i DDCM, Fermi-2 1.0-26 2766W/0051W, 05/07/84 l l

1.4 LIQUID RADI0 ACTIVITY MONITORING SYSTEM FIGURE 1.4-1 is a schematic of the Liquid Radioactivity Monitoring System showing the release points to the unrestricted area. 3 J r i 4 1 4 4 i 4 l ODCM, Fermi-2 1.0-27 2766W/0051W, 05/07/84 -, _.... _ _ _ -.,. _.. ~

FIGLRE 1.4-1 Liquid Radioactivity Monitoring System 3 4 E G ~ 11, l!! QG

  • f~

6 E Se Q 8 eg I C 3 y=\\ ) a )g s L ---- X g j i I! a (!! ...c. - e Ii EG i * 'g \\M HUFuh l l' S a -lTM*l-e3 C )! ab e it i *c; i -m a 0 z -p y o mi h 1 FMa g ) ~ 3 i [e 4 i j J- ~$ 3'a e f

Dll i*

e c: my a ig a v v ben o ' b d4 'O ge Q Ld s8 g a, - -* W \\ 0004 Fermi-2 1.0 28 27d/0051W, 05/07/84

l SECTION 2. GASEOUS EFFLUENTS 2.1, GASEOUS EFFLUENT MONITOR SETPOINTS The' gaseous monitor setpoint values determined in the following sections will be regarded as upper bounds for the actual setpoint adjustments. That is, setpoint adjustments are not required to be performed if the existing setpoint level corresponds to a lower count rate than the calculated value. Setpoints may be established at values lower than the calculated values if desired. 1 If no release is' planned for a particular pathway, the monitor setpoint should be established as close to bcekground as practical to prevent spurious alarms yet alarm should an inadvertent release occur. If a calculated setpoint is less than the monitor reading associated with e particular release pathway, no release may be made under current conditions. Under such circumstances, the number of simultaneous release pathways may be reduced or contributing source terms may be reduced and the setpoint recal-culated. 2.1.1 REACTOR BUILDING EXHAUST PLENLN, STANDBY GAS TREATMENT SYSTEM, RADWASTE BUILDING VENTILATION, SERVICE BUILDING VENTILATION, TURBINE BUILDING VENTILATION, APO ONSITE STORAGE BUILDING VENTIALATION EXHAUST RADIATION MONITORS Monitors: D 11 - N407; D 11 - N406A and B; D 11 - N403; l l D 11 - N405; D 11 - N404; and D114508 l For the purpose of implementation of Technical Specification 3.3.7.12, the alarm setpoint level for these noble gas monitors will be calculated as follows: C = monitor reading of the noble gas monitor at the alarm setpoint S concentration., (B x SF) x RtxDTB C3 = the lesser of g or (B x SF) x R xD s ss i ODCM, Fenni-2 2.0-1 2673W/0051W, 05/24/84 w - s. r.--n .-,n-,.r -s-nw..-, ---,--w-,--~~-m,-,-w,w,,,- ma - ---.,--,,-.mr.an,..,

SF = safcty fact'r; o consery;tive factor cpplied to cach nobis g:s monitor to compensate for statistical fluctuations and errors of measurement. (For example, ' SF = 0.5 corresponds to a 100 percent variation.) B = an administrative allocation factor applied to apportion the release setpoints among all gaseous releada discharge pathways to Assure that release limits will not be exceeded by simultaneous releases. Allocation factors may be assigned any desired value as long as the total of all allocation factors for all simultaneous release pathways does not exceed 1. (For ease of implementation, 9 may be set equal to 1/n, where n is the number of simultaneous final gaseous release points.) kB = Dose rate limit to the total body of an individual which is 500 mrem / year. R = monitor reading per mrem /yr to the total body t =C+ X/Q [(Ki Q) Rt i i C = monitor reading of a noble gas monitor corresponding to the grab sample radionuclide concentrations taken in accordance with RETS Table 4.11.2.1.2-1. For batch releases the sample must be taken prior to release; for continuous releases the sample is taken during the release. The monitor response corresponding to the measured concentration is determined from the monitor calibration curve for the particular monitor. 775 = the highest annual average relative concentration at the site boundary. (if desired, the annual average relative concentration at the site boundary for the particular release point may be used.) -0 = 4.186 x 10 sec/m in the NW sector. ODCM, Fermi-2 2.0-2 2673W/0051W, 05/24/84

t ' K.. a t:t:1 body dose factor due to gamma emissions from radionuclide i g 3 Q. (mrem /yr per pCi/m ) from Table 2.1-1. n. g .= rate-of release of noble. gas radionuclide.1 (pCi/sec) from the release pathway-under - considerations the product of. X and iy F, where X -is the concentration of radionuclide i for the y gy particular. release ' volume and F -is the release flowrate. (X1y y 1,n pCi/cc and F in ec/sec.) y NOTE T 1 .b For all radiation monitor setpoint determinations assume a fixed flow rate which corresponds to the maximum flow rate for' a particular release pathway. The applicable flow rate values for ute in determining radiation monitor setpoints are"found in Table 2.1-2. Dose rate limit to the skin of the body of an individual in an D = ss unrestricted area which is 3000 mrem / year. m nitor reading per mrem /yr to the skin R = s '(L + 1.1 M ) Qi C + X7Q [ R i 1 = s 1-skin dose factor due to beta emissions from radionuclide 1 (mrem /yr L = i per pCi/m ) from Table 2.1-1. mrem skin dose per mrad air dose 1.1 = air dose factor due to gamma emissions from radionuclide 1 (mrad /yr M = y 3 i per pCi/m ) from Table 2.1-1. i l l' ODO4, Fermi-2 2.0-3 -2673W/0051W, 05/24/84 1 a.

2.1.2' CONTADNENT DRYWELL PURGE The containment Drywell Purge is a batch-type release which discharges to either the Reactor Building Exhaust Plenum or the Standby Gas Treatment System in accordance with Technical Specification 3.11.2.8. If, based on sample analysis results, a decision is made to route the discharge through the Standby Gas Treatment System, the treated effluent will be monitored by the Standby Gas Treatment System Monitor. l However, if a decision is made to route the discharge through the Reactor Building Exhaust Plenum, the setpoint for the Reactor Building Exhaust Plenum effluent monitor must be redetermined to account for the source term associated with the drywell purge. This is accomplished by following the methodology of Section 2.1.1, with the following exception: Q must be replaced with a new source term, Q I f CR where QCR

  • Qi+91 and where qi =

the drywell purge source term, which is the radionuclide concentration multiplied by the planned drywell purge release rate. 0004, Femi-2 2.0-4 2673W/0051W, 05/24/84

U = the consumption rato cf fresh leafy vegetation by the receptor in g age group a, in kg/ year. (See Table 2.2-10)) U = the consumption rate of stored vegetation by the receptor in age group a, in kg/ year. (See Table 2.2-10)) f =t fraction of the annual intake of fresh leafy vegetation grown g locally. (1.0) f = the fraction of the annual intake of stored vegetation grown locally. g (0.76) t = the average time between harvest of leafy vegetation and its consump-tion in seconds. 4 (8.6 x 10 ) t = the average time between harvest of stored vegetation and its consump-h tion in seconds. 6 (5.18 x 10 ) Y = the vegetation areal density, in kg/m. (2.0) y (DF ), = the organ ingestion dose factor for the ith racionuclide for the receptor in age group (a), in mrem /pC. from Tables 2.2-5 through 2.2-8. = the decay constant for the ith radionuclide, in sec-1 1 1 A = the decay constant for removal of activity on leaf and plant sur-faces by weathering, 5.73 x 10-7 ~1 sec (corresponding to a 14 day half-life). 0004, Fermi-2 2.0-20 2673W/0051W, 05/24/84

'Fcr tritium in vegetation, the' vegetation path::y fcctor is a special cas3 due to the fact.that the concentration of tritium in vegetation is based on air-borne concentration rather than deposition: as g) (OFL ), [0.75(0.5/H)] (mrem /yr per pCi/m ) R,gp) = K'K"(U I gg+U f where: 3 K'", = a constant of unit conversion,10 gm/kg. H = absolute humidity of the atmosphere, in gm/m. (8) 0.75 = the fraction of total vegetation that is water. 0.5 = the ratio of the specific activity of the vegetation water to the atmospheric water. and other parameters and values are given above. ODCN, Fermi-2 2.0-21 2673W/0051W, 05/24/84

2.2.3 METHODOLOGY FOR GASEOUS DOSE PRO E CTIONS (To Determine Necessity of Operating Gaseous Radwaste Treatment System) i The W C requires that dose projections be performed to indicate whether cumu-lative doses over a thirty-one (31) day period are likely to exceed 25% of the annual design objective dose limit adjusted to a thirty-one (31) day period. The.25% actuation levels of 0.3 mrem to any organ, 0.2 mrad gamma air dose, and 0.4 mr.ad, beta air dose were selected by the MC based on their When the thirty-one cost-benefit analysis for operation of radwaste systems. (31) day projected dose exceeds 0.3 mrem to any organ, 0.2 mrad gamma air dose or 0.4 mrad beta air dose, operation of appropriate portions of the radwaste systems would be required. When the percent of the quarterly limit exceeds 4% for any organ, gamma air dose or beta air dose (i.e., the cumulative organ dose exceeds 0.3 mrem, the cumulative gamma air dose exceeds 0.2 mrad or the cumulative beta air dose exceeds 0.4 mrad) determine the thirty-one (31) day dose projection as follows: yair(prj) --yair(accumulated) Xb31) U X Sair(accumulated) 31

  • .2 hair (prj)

X tb(accumulated) 31] tb(prj) X f 0 (accumulated) ~ ~~ o X 3( f D (prj) o s t where = the cumulative total air doce due to gamma j DYair(accumulated) emissions for the current quarter plus the release .i under consideration for the particular reactor i unit. l J 2.0-22 O(XN, Femi-2 2673W/0051W, 05/24/84 1 . - _ = _ _. -. -... - -,.. - -.. - -, -,,.,..,

4 e the cumulativa total air dose due to b:;t2 D ':ir(tecumultted) S - emissions for the current quarter plus the release under consideration for the particular reactor f unit. the cumulative total body dose for the elapsed D = tb(accumulated) portion of the current quarter plus the release under consideration for the particular reactor unit. the cumulative organ doses for the elapsed portion D (ac u ulated) = o of the current quarter plus the release under consideration for the particular reactor unit. the number of days into the current quarter to the X = nearest whole day. If activities planned during the remainder of the 31-day period are expected to contribute a significant dose and the determination can be reasonably made, this contribution should be included in the equations: Dyair(accumulated)

  • 31

+ D yair(prj) J X anticipated 3 air (accumulated) ~' 31 + D hair (prj) X anticipated tb(accumulated) x ~31 . D X anticipated D = tb(prj) D (accumulated) '~ o X 3l D (prj) X anticipated o where i l D = the anticipated organ dose resulting from anticipated anticipated operational occurrences which may occur in addition to routine releases over the thirty-one (31) day period. I l ODCM, Fermi-2 2.0-23 l 2673W/0051W, 05/24/84 1 -a

If, yair(prj) > 0.2 mrad or D ( ) > 0.4 mrad then appropriate portions of the Gaseous Radwaste System shall be used to reduce radioactive materials in gaseous waste prior to their discharge. "if, Dtb(prj) > 0.3 mm or D (prj) > 0.3 mm o then appropriate portions of the Ventilation Exhaust Treatment System shall be used to reduce radioactive materials in gaseous waste prior to their discharge. i j T 4 ODO4,' Fermi-2 2.0-24 2673W/0051W, 05/24/84 ., /... _.. _ _ _ _ _ _., _ _ _ _ _ _ _

TABLE 2.2-1 INHALATION 00SE FACTORS FOR IWANT* j (MREM PER PCI INHALED) Page 1 of 3 Nvettet DoNE tavEn 7.000v TNva0:0 m:0NEv tous s -tts M 3 40 DATA 4.62E-07

4. 62E-07 4.62F-07 4.62E-07 4.62E-07 4.62E-07 j

C 14 1.89E-05 3.79C-06 3.79E-06 3.79E-06 3.79E-06 3.79E-06 3.79E-06 44 24 7.b4E-06 7.54E-06 7.54E-06. 7.54E-06 7.54E-06 7.54E-06 7.54E-06 P 32 1 45E-03 0.0 3E-05 S.53E-05 No DATA NO DATA NO DATA 1.1SE-05 CR 51 NO DATA MO DATA 6.39E-08 4.11E-08 9.4SE-09 9.17E-06 2.SSE-07 mm S4 NO DATA 1 8IE-05 3.56C-06 NO DATA 3.56E-06 7.14E-04 S.04E-06 .................................-.................................. ~. NN 96 NO DATA 1.10E-09 1 5tE-10 NO 04Ta 7.86E-10 S.95E-06 S.12E-05 FE SS 3.41E-05 S.39E-06

2. 3 BE-0 6 40 DATA NO DATA 6.21E-05 7.82E-07 FE 59 9.69E-06 1.68E-05 6.77E-06 40 Data 40 DATA 7.25E-04 8.77E-05 CO 58 NU DATA 0.71E-07 1 30E-06 NO 04T4 40 OATA S.SSE-04 7.95E-06 CO 60 N0 0414 5.73E-06 8 41E-06 40 DATA NC caTA 3.22E-03 2.20E-05 41 63 2 42E-04 1.46E-05
8. 2 9E-0 6 40 04TA NO DATA 3.49E-04 8.73E-06 NI 45 1.71E-09 2.03C-10 8.79E-a1 40 OATA N0 DATA S.80E-06 3.SBE-05 CU 64 NO DATA 1.34E-09 5 53E-10 40 04TA 2.04E-09 6.64E-06 1.07E-05 24 65 1.38E-05 4.47E-05 2.22E-05 NO DATA 2.32E-05 4.62E-04 3.67E-05 IN 69 3.85E-11 6.91E-11 5.13E-12 NO Oafa 2.e7E-11 1.05E-06 9.44E-06 4

04 83 NO DATA NO DATA 2.72E-07 40 DATA NO DATA NO DATA L7 E-24 pa 84 NO DATA NO DATA 2.86E-07 40 Dafa 40 DATA 40 Dafa L7 E-24 sa et 40 DATA 40 Data 1 46E-Os 40 OATA NC Data 40 DATA LT E-24 at to NO DATA 1.3aE-04 6.30E-05 NO Data NO DAfa NO DATA 2.17E-04 90 se NO Oafa 3.98E-01 2.03E-07 40 Data 40 DATA NO DATA 2.42E-07 i at 89 40 DATA 2.29E-07 1.47E-07 NO DATA 40 DATA NO DATA 4.tTE.Se la 89 2.04E-04 40 DATA 0.15C-06 NO Data NO 0414 t.45E-03 4.STE-05 la 10 2.92t-02 40 OAT A 1.05E-03 NO 0414 NO DAfa 5.03E-03 9.36E-OS SR 91 6.03E-08 40 04T4 2,4 7 E-0 9 ND 04TA 40 DATA 3.76E-05 S.24E-05 Sa 92 7.SOE-09 NO DATA 2 79E-10 40 04TA NO DATA 1.70E-05 1.00E-64 Y 90 2 35E-06 40 OATA 6.30E-Os NO DATA 40 DATA 1.92E-04 7.43E-05 7 91P 2.911-10 NO DATA 9.90E-12 40 DATA NC 041A 1.99E-04 1.6 tE-06 7 91 4 20E-04 es0 04Ta 1.12E-05 40 CATA NO DATA t.75E-03 S.02E-05 Y 92 8.17E-04 NO DATA 3.29E-10 m0 DATA NO Data 3.7st-05 9.04E-05 i h i l 1 i Reference 3, Table E-10. l .i ODO4, Fermi-2 2.0-25 2673W/0051W, 05/24/84 3 ( . ~.

TABLE 2.2-1 CONT'D INHALATION DOSE FACTORS FOR IPFANTO (MREM PER PCI INHALED) Page 2 of 3 e ssUCol cE.. so4E (svEn T.soor TNvn0:0 agoNEv tvec ar.tti I V 93 3 07E-07 NO DATA 2.91E-09 ' NO DAT A NO DATA 5 46E-05 1.19E-04 24 95 8.24E-0> I.99E-05 1 45E-05 MO DATA 2.22E-05 1.25E-03 1.55E-05 i 24 97 1.07E-07 I.83E-OS 8.36E-09 40 DATA 1.SSE-08 7.88E-05 1 00E-04 WB 95 1 12E-05 4.59E-06 2.70E-06 NO DATA 3.37E-06 3.42E-04 9.05E-06 NO 99 NO DATA 1.186-07 2.31E-04 NO DATA 1.ASE-07 9.63E-05 3.48E-05 IC 99m 9.90E-13 2.06E-12 2.66E-11 40 DATA 2.22E-11 5.79E-07 1 45E-06 7C101 4.65E-14 5.98E-14 5.SOE-13 NO DATA 6.99E-13 4.17E-07 6.03E-07 aut03 1 44E-04 NO DATA 4.85E-07 NO DATA 3.03E-06 3 94[-04 1.15!-05 AU105 8.74E-10 NO DATA 2.93E-10 NO DATA 6 42E-10 1.I2E-05 3 46E-05 AUl06 6.20E-05 NO DATA 7.77E-06 NO DATA 7.61E-05 8.26E-03 1 17E-04 AG1104 7,13E-06 5.16E-06 3.57E-06 40 DATA 7.SOE-06 2.62E-03 2.36E-05 TE125m 3 40E-06 1.42E-06

4. 70 E-0 7 1.16E-06 NO DATA 3.19E-04 9.22E-06 TE1277 1 19E-05 4.93E-06 1 4sE-06 3.48E-06 2.6tE-05 9.37E-04 1.95E-05 TE127 1.59E-09 6.81E-10 3.49E-10 1.32E-09 3.47E-09 7.39E-06 1.74E-05 TE129* 1.Plf-05 4.35C-06 1 59E-06 9.91E-06 2.27E-05 1.20E-03 4.93E-05 TE129 5.63E-11 2.4eE-11 1.34E-11 4.82E-11 1 25E-10 2.14E-06 1.SSE-05 TE131m 7.62E-08 3.93E-08 2.59E-08 6.38E-08 1 09E-07 1 42E-04 8.51E-05 FE131 1 245-11 5.0?E-12 3.57E-12 1.13E-11 2 85E-11 1.47E-06 5.A7E-06 7E132 2.66E-07 1.69E-07 1.26E-07 1.99E-07 7.39E-07 2.43E-04 1.15E-05 3 330 4.54E-06 9.91E-06 3.90E-06 1 14E-03 1.09E-05 NO DATA 1.42E-06 i

1 131 2.71E-05 3.17E-05 1.40E-05 1.06E-02 3 70E-05 NO DAT A 7.56E-07 I 132 1.21E-06 2.53E-06 0.99E-07 1.2tE-04 2 92E-06 NO DATA 1.36E-06 8 133 9.46E-06 1.37E-05 4.00E-0 6 2.54E-03 1 60E-05 NO DATA t.54E-06 8 134 6.50E-07 1 34E-06 4.75E-07 3.18E-05 1 49E-06 NO DATA 9.21E-07 I 135 2.76C-06 5.43E-06 1.99E-06 4.9?E-04 6.05E-06 NO DATA 1.31E-06 C5134

2. 8 3 E-04 5.02E-04 5.32E-05 NO DATA 1.36E-04 5.69E-05 9.53E-07 C5136 3 45E-05 9.6tE-05 3.78E-05 NO DATA 4 03E-05 S.40E-06 1.02E-06 C5137 3.92E-04 4.37F-04
3. 25 E-0 5 NO DATA 1 23E-04 5.09E-05 9.53E-07 E5138 3.61E-07 5 5s[-n7 2.84E-07 NO DATA 2.93E-07 4.67E-Os 6.26F-07 e4:39 1.06E-09 7.03E-13 3.0FE-11 NO DATA 4.73E 13 4.25E-06 3.64E-05 I

l 2.0-26 0004, Fe11ni-2 2673W/0051W, 05/24/84

TABLE 2.2-1 CONT'D INHALATION DOSE FACTORS FOR INFANT * (MREM PER PCI INHALED) Page 3 of 3 l ensct:0E So4E t a vEn t.toor TNya0:0 at0NEv toma sr.tti 1 04:40 4.00E.05 4.00E-08 2.07E.06 NO DATA 9.59E.09 1.14E-03 2 74E.05 04141 1.I2E-10 7.70f-14 3.55E-12 40 DATA 4.64k-14 2.12E-06 3 39E-06 04142 2.84E-11 2.36!-14 1.40E-12 NO DATA 1 36E-14 1.11E-06 4.95E-07 (4140 3 6tt-07 1 43t-07 3.68E-08 NO DATA No DATA 1 20E-04 6.06E-05 L A142 7.36E-10 2 69E-10 6.4*E-11 NO DATA NO DATA S.87E-06 4.25E-05 CEt41 1.90E-0> 1.19E-05 1 42E-06 40 DATA 3.754-06 3 69E-04 1.54E-05 CE143 2 39E-07 1.90E-07 1.59E-08 NO DATA 4.03E-04 8.3CE-05 3 55E-05

  • E144 2 28E-03 8.e5E-04 1.26E-04 NO DATA 3.04E-04 7.03E-03 1.06E-04 Pat 43 3.00E-05 3.74E-06 4.9?E-07 40 Daft 1 41E-06 3.09E-04 2 66E-05 Pa t44 3 4fE-11 1.32E-!!

1 72E-12 NO DATA 4.40E-12 1.15E-06 3 06E-06 N0147 5.67E-06 5.01F-06 3.57E-07 No 0ATA 2 25E-06 2.30E-04 2 23E-05 N 887 9.26E-09 6.44E-09 2 23E-09 NO DATA NO DATA 2.83E-05 2 54E-05 NP239 2.65E-07 2.37E-08 1 34E -0 8 NO 041A 4.751-08 4.25E-05 8.78E-05 t I l 2.0-27 0004, Fermi-2 2673W/0051W, 05/24/84 c l .._,.,m._,._ ,-.,_,._...-..._,m,

TABLE 2.2-2 INHALATION 00SE FACTORS FOR CHILDS (MREM PER PCI INHALED) Page 1 of 3 Liven T.Sepr TNya0!O RIONEY LUNG GI-LLI NUCLIGE... SONE................................. ...................................1.04E-07 l N 3 NO DATA 3.04E-97 3.04E-O F 3 04f-07 1.040-07 3 04E-01 C to 9.70E-06 1.62E-06 1.62E-06 8 22E-06 1.52E-06 1 82E-06 1 82E-06 NA 24 4.35E-06 4.35 -06 4.3sf-06 4.3bE-06 4.35E-06 4.35E-06 4.35E-06 i P S2 7.04E-04 1.09E.05 2.6 T C-0 5 NO DATA NO DATA NO DATA 1.14E-05 Ca 51 NO DATA NO DATA 4.17E-Os 2 31r.04 6.57E-09 4.59E.06 2 93E-01 NN 54 40 DATA 1.16E-05 2 57E-06 NO DATA 2.71E-06 4.26E.04 6.19F-06 ..........................................................................3.33C-05 NN 56 40 DATA 4.48!-10 S.43E-11 NO DATA 4.52E-10 3.55t-06 i FE 55 1.2eE-05 6 80E-0e

2. t G E-0 6 NO DATA NO DATA 3 00E-05 7.75E-07 ft 59 5.S9C-06 9.G4E-06 4.5tC-06 40 OATA NO DATA 3 43[.04 1 9tt-05 C0 SS 40 DATA 4.T9E-07 8.55E-07 N0 DaT4 NC OATA 2.99E-04 9.29E-06 I

CD 60 NO DATA 3 55E-06 6.12E-06 40 DATA ND DATA 1.9tE-03 2 60E-05 NI 63 2 22E.04 1.25E-05 7.56E-06 NO DATA NO DATA 7.43E-05 1 7tE-06 NI 65 8.08E.10 7.99E-11 4.44E-11 No DATA NU OATA 2 2tE-06 2.27E-05 ~ CU 64 NO DATA 5.39E-10 2.90C-10 40 OATA 1 63E-09 2 59E-06 9.92E-06 2h 6% t.tSE-05 3.06E-05 1.90E-05 40 DATA 1 93E-05 2.69E-04 4.41E-06 j 2N 69 1.81E-11 2 61E-11 2.410-12 NO DATA 1.58E-11 3.84E-07 2.75E-06 i na 33 NO DATA NO DATA 1.20E-07 40 DATA NO DATA NO DATA LT E-24 4 et R4 NO DATA Nu OATA 1.4RE-07 40 CATA NO DATA NO DATA LT'E-24 I f9 SS NO Oafa NO DATA

6. 04 E-0 9 NO DATA 40 OATA NO DATA LT E-24 j

en A6 NO DATA 5.36t-05 3.09E.03 40 DATA NO DATA NO DATA 2.16E.06 at 88 NO DATA 1.5 2 E- 0 T 9.90!.08 NO DATA NO DAfa NO DATA 4.665 09 j a5 39 NO CaTA 9.33E.08

7. 8 s E.0 4 NO DATA NO DATA NO DAT A 5.llE-10 4

J St 39 1.62E-04 NO DATA 4.66E.06 NO DATA NO DATA 5.81E-04 4.52E-05 la 90 2.73E-02 ND DATA 1.74E-03 NO DATA NO DATA 3 99t.03 9.2BE-05 i SP 91 3 20E-09 NO D AT A

1. 2 4 E-0 9 40 DATA NO DATA 1 44E-05 4.70E-05 j

la 92 3.44E-09 NO DATA 1.42E-10 40 DATA NO DATA 6.49C-06 6.55E-05 v 90 1.!!E-06 NO DATA 2.94F-08 NO DATA NO DATA 7.07E-05 7.24E-05 j Y 9tr 1 1TE-10 NO DATA 4.9sE-12 40 DATA NO DATA 7.60F-07 4.64E-07 Y 98 2 47E-04 40 OATA

6. 5 9E -0 6 NO DATA No caTa 7.10E-04 4.97E-05 v 92 5.50E-09 NO DATA t.5 f f-10 40 DATA NO DATA 6.46E-C6 6.46E.c5 j

s i J Reference 3, Table E.9. 8 I 1 2.0-28 ODCN, Fermi-2 2673W/0051W, 05/24/04 m,.

TABLE 2.2-2 CONT'D INHALATION DOSE FACTORS FOR CHILD

  • i (MREM PER PCI INHALED)

Page 2 of 3 evCtt0E Oost tsven 7.6oor 7 men 010 stoNEv tugs st-Ltt v 93 S.04E-Os 40 0a76 1 3er-09 N0 Da7a NO Da74 2.0:f-05 1 0SE-04 2R 95 S.13E-OS 3.13E-0$ t.00E-OS NO DATA 3.6ti-05 6.03E-04 1 6SE-05 28 97 S.07C-08 7.34E-09 4 32E-09 NO Da74 1.0SE-06 3.06E-05 9.49E-05 No 96

6. 3 SE-06 2.48E-06 3 77E-06 40 Da7A 2.33E-06 8.66E-04 1.00E-05 NO 99 40 DATA 4.66E-OS
1. t >E-O s NO Daft 1.06E-07 3.66E-05 9.42E-OS TC 99P 4.tlE-13 9.410-13 1.S6E-Lt NO DATA 1.37E-11 2.57E-c7 8 30E-06 7C101 2 19E-14 2.30E-14 2 91E-13 NO 0474 3 92E.13 t.SAE-07 4.418-99 l

Auto) 7.S$f-07 NO DATA 2 90E-07 NO DATA 1.90E-06 1.79E-04 1.21E-05 au1OS 4.13E-10 NU 0474 1 50E-10 40 DATA 3.63E-10 4.3nt-06 2.69E-OS AUl06 3 68E-05 NU OafA 4.S7E-06 NO DATA 4.97E-05 3.87E-03 1.16E-04 AC110* 4.56E-06 3 08E-06 2.47E-06 NO DATA S.74L-06 1.48E-03 2 71E-OS TE1259 1.82E-06 6.29E-07 2 47E-07 S.202-07 NO DATA 1.29E-04 9.13E-06 TE127m 6.72E-06 2.3tE-On 8 19E-07 1.64E-06 1 72E-05 4.00C-04 1.93E-OS TE127 7.49E-10 2 57E-10 1 6SE-10 S.30E-10 1 9tt-09 2.7tF-06 1.52E-05 TEt21* S.19E-C6 1.86E-06 8.22E-07 1.7tt-06 1.166-C5

4. 76C-04 4.9tE-05 TE129 2.64E-Il 9.4SE-12 6.44C-12 1.93E-11 6.94L-11 7.9tE-07 6.89E-06 TE1317 3 63E-08 1.60E-00 1.37[-00 2.64E-00 1 08E-07 S.54E=0S 8.32E-OS VE131 S.87E-12 2.20E-12 1.70C-12 4.59t-12 1 19C-It S.SSE-07 3.60E-07 t

TE132 1.30E-07 7.36E-00 7.12 E-O s 8.SSE-08 4.79L-07 1.02E-04 3.72E-05 I 130 2 21E-06 4.43E-06 2 28E-06 4.99E-04 6.6tt-06 NO Oafa 1.3st.06 8 131 1 30E-05 1 30E-OS 7 37E-06 4.39f-03 2 13E-05 NO 0474 7.68E-07 l 3 132 S.72E-07 1.10E-06 S.0FE-07 S.23E-05 1 69E-C6 NO Cafa s.4SE-07 i i 133 4.40C-06 S.49*-06 2.00E-06 1.04E-03 9 13E-06 NO Defa 1.48E-06 i i 134 3.ITE-07 S.84!-07 2 69E-07 1.37E-05 8.92E-07 NO DA(A 2.SSE-07 1 135 1 33E-06 2.l6E-06 1.12 E-0 6 2.14t-04 3.62E-06 NO Da7A 1.20E-06 i cst 34 l.76E-04 2.74C-04 6.0 f f -0 5 40 DafA 8.93E-OS 3.27E-05 1.04E-06 Clite 1.76E-OS 4.62E-Ob 3.14E-05 40 DATA 2.SSE-05 3.93E-06 1.13E-06 i cst 37 2 4SE-04 2.23E-04 3.47E-05 40 Dafa 7.63E-05

2. Sit-0$ 9.7eE-07 I

C$tle 8 74E-07 2.27E-07 1.$0E-07 N0 DATA 1 6tE-07 1 04E-08 7.29E-08 l ast39 4.9st-10 2.66*-13 1.4SE.l t 40 Da7 A 2.13E-13 1.S6E-06 s.S6E.0% t i i i 0004, Fermi-2 2.0-29 i 2673W/0051W, 05/24/84 I t -v---se n. -,n, .m,,-,.-, .m ,w.m,_nn,--_ wmm,-.. -m me,-- -m mw -

TABLE 2.2-2 CONT'D INHALATION DOSE FACTORS FOR CHILD * (MRO4 PER PCI INHALED) Page 3 of 3 seuCL lut. Buset L19E4 7.000f TNYe080 EIDesEY LussG GI-LLI 84140 2 00E-0) 1.75E-08

3. 3 7E-0 6 NO DATA 5.71E-09 4.7tE-04 2.75E-05 Sat 41 5.29E-11 2.95E-14 1.72F-12 M0 DATA 2.56E-14 7.89E-07 7.44E-08 34147 1.35E-11 9.73E-15 7.54E-13 NO CATA 7.87E-15 4.44E-07 7.41f-10 Lat40 1.74E-07 6.08E-08 2 04E-0 8 NO DATA NO DATA 4.94E-05 6.10E-05 L A !'2 3.50E-10 1.llE-10 3.49E-11 NO DATA NO Data 2.35E-06 2.05E-05 CEL41 1.06E-OS 5.20E-06
7. 8 3 E-0 7 NO DATA 2.3tt-06 1.47E-04 1.53E-05 CE143 9.89E-08 5.37E-08
7. 7 7E-0 9 NO DATA 2.26E-08 3.12E-05 3.44E-05 CE144 1.83E-03 5.72E-04 9.77E-05 40 DATA 3.17E-04 3.23E-03 1.05E-04 P4843 4.99E-06 1.50E-06 2 47E-0 7 NO DATA 8.11k-07 1.17E-04 2.63E-05 Pat 44 1.6tt-11 4.996-12 8 10E-13 40 DATA 2.64E-12 4.23E-07 5.32E-08 40147 2.92E-06 2.36E-06 1 84E-07 NO DATA 1.30E-06 8.876-05 2.22F-05 w 187 4.41E-09 2.6tt-09 1 17F-09 NO DATA NC OATA 1.1tE-05 2.46E-05 NP239 1.76E-07 9.04f-09 6.35E-0 9 m0 DATA 2.43E-08 1.57E-05 1 73E-05 I

i 0004, Fermi-2 2.0-30 2673W/0051W, 05/24/84 ---~.,---------------.---,-----,,..---.---,,...-nr.,--.~n,,---,--_.- ..e-n~rn~- e-

TABLE 2.2-3 INHALATION DOSE FACTORS FOR TEENAGERS (WEM PER PCI INHALED) Page 1 of 3 l Nuctics. DONE LevEn v.s0cv TNyaciO a:ONEv tvNc st-tti i a 3 NO DATA 3.59E-07

1. 5 9f =0 7 1.59E-07 1.59F-07 3.59E-07 1.59E-07 C 14 3.2bE-06 6.C9E-07 6.09E-07 6.09E-07 6.P9E-07 6.09E-07 6.09E-07 NA 24 1.72E-06 3.72E-06 1.72E-06 1.72E-06 1.72E-06 1.72E-06 1.72E-06 P 32 2.36E-04 1.57C-03 8.95 E-0 6 40 DATA NC OATA NO DATA 1.16F-05 CR St NO DATA NO DATA 1.69F-08 9.37E-09 3.84E-09 2.62E-06 3.75E-07 mm 54 NO DATA 6.39E-06
1. 03 E-0 6 NO DATA 1.59E-06 2.40E-04 8.35E-06 MN 56 N3 OATA 2.12i-10 3.15E-11 40 DATA 2.24E-10 1.90E-06 7.18E-06 FE 55 4.tSE-06 2.90E-06 6.93E-07 NO DATA NO DATA 1.55E-05 7.99E-07 FE 59 1 19E-06 4.62E-06 1.79E-06 NO DATA NO DATA 1.91E-04 2.23E-05 CO St 40 DATA 2.S9f-07 3.47E-07 NO DATA NO DATA 1.68E-04 1.19F-05 CU 60 NO DATA 1.87E-C6 2.4 8 E-0 6 NO DATA NO DATA t.09E-03 3.24E-05 NI 63 7.25E-05 5.43E-06 2.47E-06 NO DATA NO DATA 3.84E-05 1 77E-06 NI ob 2.73E-In 3.e6E-11 1.59E-it 40 OATA NO DATA 1.17E-06 4.59E-06 CU 64 40 DATA 2.54E-13 1.06E-10 40 DATA 8.01E-10 1.39E-06 7.68E-06 IN 65 4.82E-06 1.o7E-05
7. 8 c E-0 6 No DATA 1.08E-Ob I.55E-04 5.83E-06 EN 69 6.04E-12 1.15F-It 8.07E-13 NO DATA 7.53E-12 1.90E-07 3.56F-08 na 83 NO DATA NO DATA 4.30C-08 NO DATA NO DATA NO DATA LT E-24 et 84 NO DATA NU CATA 5.4tE-08 40 DATA NO DATA NO DATA LT E-24 A4 Ob NO DATA NO CATA
2. 2 9E-0 9 NO DATA NO DATA NO DATA LT E-24 48 to NO DATA 2.38E-05 1.05E-OS 40 DATA NO DATA NO DATA 2.2tE-06 a? 88 40 DATA 6.82E-08 3.4 0E -0 8 NO DATA NO DATA NO DATA 3.65E-15 48 89 NO DATA 4.407-08 2.9tE-08 NO DATA NO DATA 840 D ATA 4.22E-17 SR 89 5.43E-05 NO DATA 1.56E-06 NO DATA NC OATA 3.02E-04 4.64E-05 54 93 1.35E-02 NO DATA 8.35E-04 NO DATA NO DATA 2.06t=03 9.56E-05 SR 91 1.10E-08 NO CATA 4.39E-RO NO DATA NO DATA 7.59E-06 3.24E-05 i

l 54 92 1.19E-C9 NO CATA 5.08E-It 40 DATA NO DATA 3.43E-06 1.49E-05 Y 90 3.73E-0T NO DATA 1 00E-08 NO DATA NO DATA 3.66E-05 6.99E-05 Y 9t* 4.63E-Il NO DATA t.7TE-12 NO DATA NO DATA 4.00E-07 3.77E-09 Y 91 8.26E-05 No DATA 2.2tE-06 NO DATA NO DATA 3.67E-04 5.tlE-05 Y 92 8.84E-09 WO DATA 5.36E-ti NO DATA NO DATA 3.35E-06 2.06E-05 Reference 3, Table E-8. l l l 2.0-31 ODO4, Fermi-2 2673W/0051W, 05/24/84 1 ~

TABLE 2.2-3 CONT'D INHALATION DOSE FACTORS FOR TEENAGERS ( EEM PER PCI INHALED) Page 2 of 3 8euCLiet DONE LIvf 4 7.000v TNva010 al0Niv LUseG Cl-LLI V 93 "' 1 69E-08 40 DATA

4. 45 E-10 40 DATA NO DATA 1.04E-05 7.24E-05 24 95 1.82E-05 5 73E-06
3. 94 E-06 40 DATA S.42E-06 3.36E-04 1 56E-05 l

2a 17 1 72E-08 3 40E-09 1.57 E-0 9 NO DATA 5.15E-09 1.62E-05 7.8SE-05 40 96 2 32E-06 1 29E-06 7.0SE-07 NO DATA 1.25E-06 9.39E-05 1.21E-05 WD 99 NO DATA 2 11E-Os 4.03E-09 NO DATA 5.14E-08 1.92E-C5 1 36E-05 1C 998 3 73E-13 4.83E-11 6.24E-12 NO DATA 7.20E-12 1 44E-07 7.66E-07 TC101 7.40E-15 1.0SE-14 1.03 E-13 NO DATA 1 90E-11 8.34E-Os 1.09E-16 aul03 2.63E-07 NO CATA 1 12E-07 NO DATA 9.29E-07 9.79E-05 1.36E-05 4U105 1.40E-10 NU OATA 5.42E-11 NO DATA 1.76E-10 2.27E-06 1 13E-05 4U106 1.23E-05 NO DATA

1. 55 E-0 6 NO DATA 2.30E-05 2.01E-03 1.20E-04 66110p 1.73E-06 1.64E-06 9.99E-07 40 DATA 3.13E-06 0.44E-04 3 41E-05 TE124* 6.10E-07 2 00E-07 8.34E-08 1.75E-07 N0 DATA 6.70E-05 9.38E-06 TE127m 2.25E-06 1.C2E-06 2.73E-07 5 4tE-07 8.17E-06 2 0FE-04 1.99E-05 fil27 2 51E-10 1 14F-10 5.52E-11 1.77E-10 9.10E-10 1 40E-06 1.01E-05 TE1299 1.74E-06 0.23E-07
2. 81 E-0 7 5.72E-07 6.49E-06 2 47E-04 5.06E-05 TE129 8.87E-12 4.22E-12 2.20E-12 6 4RE-12 3.12E-11 4.82E-07 2.02E-07 IE131* 1 23E-00 7.51E-09 5.03E-09 9.06E-09 5.49E-08 2 97E-05 7.76E-05 TE131 1 97E-12 1.04E-12 6.30E-13 1 55E-12 7.72E-12 2 92E-07 1.89E-09 TE132 4 50E-Os 1.e3E-08 2.74E-08 3.07E-00 2.44E-07 5.61E-05 5.79E-05 8 130 7.80E-07 2.24E-06 8.96E-07 1 06E-04 3 44E-06 NO DATA 1.14E-06 I 131 4.43E-06 6.14E-06 3.30E-06 1.03E-03 1.05E-05 NO DATA 8.11F-07 1 132 1.99E-07 5.47E-07
1. 9 7 E-0 7 1 89E-05 8.65E-07 NO DATA 1.59E-07 8 133 1 52E-06 2.36E-06 7.7tE-07 3.65E-04 4.49E-06 NO DATA 1.29E-06 1 134 1.11E-07 2.90E-07
1. 05 E-0 7 4.94E-06 4.58E-07 h0 DATA 2.55E-09 1 135 4.62E-07 1.10E-06 4.36E-07 7.76E-05 1.06E-06 NO DATA 8.69E-07 C1134 6 281-05 1.41E-04 6.Ont-05 NO DATA 4.69E-05 1.83E-05 1.22E-06 C5116 6.44E-06 2.42E-05 1.71E-05 NO DATA 1.30E-05 2.22E-06 1.36E-06 C1137 8.30E-05 1.06E-04
3. 09 E -0 5 NO DATA 3.80E-05 1.51E-05 1.06E-06 C1138 5.42E-08 1.07E-07 5.S e t-O s NO DATA 8.28E-OS 9.04E-09 3.30E-11 84839 1.67E-10 1.1BE-13 4.87E.12 40 DATA 1.11E-13 0.0eE-07 S.06E-07 2.0-32 0004, Fermi-2 2673W/0051W, 05/24/84

4 TABLE 2.2-3 CONT'D Ift!ALATION DOSE FACTORS FOR TEENAGER

  • l (MREM PER PCI INHALED)

Page 3 of 3 t. 8epCL10t DONE Livit T. 000V THYROIS EloseEV LussC GI-LLI 04140 6.84E-06 S.3SE-09 4.40E-07 NO DATA 2.SSE-09 2.54E-04 2.86E-05 54141 1.TSE-11 1.s2E-14 5.9AE-13 NO DATA 1.23E-14 4.ttE-07 9.33E-14 64142 4.62E-12 4.6 3E-15 2.84E-13 NO DATA 3.92E-15 2.39E-07 5.99E-20 L4140 5 99E-00 2.95E-OS 7.42E-09 NO DATA NO DATA 2.68E-05 6.09E-05 LA142 1.20E-10 5.31E-11 1.32E-11 NO DATA 90 OATA 1.27E-06 1 50E-06 CE141 3.55E-06 2.37E-06 2.71E-07 N3 OATA 1.11E-06 7.67E-05 1.58E-05 Cele) 3 12E-05 2.42E-08 2.70E-09 NO DATA 1.08E-OS 1 63E-05 3.19E-05 CE144 6.11E-04 2.53E-04 3.2st-05 NO DATA 1.51E-04 I.67E-03 1 00E-04 P9143 L.67E-06 6.64E-07 8.28E-08 NO DATA 3.06E-07 6.04E-05 2.67E-05 Pat 44 5.37E-12 2.20E-12 2.72E-13 40 DATA 1.26E-12 2.19E-07 2 94E-14 N0147 9.03E-07 1.07E-04 6.41E-08 40 DATA 6.29E-07 4.65E-05 2.20F-05 w 387 3.50E-09 1.22E-09 4.29E-10 NO DATA NO DATA S.92E-06 2.21E-05 w239 4.23E-os 3.99E-09 2.21E-09 se0 Data 1 25E.De s.11E-06 1 65E-05 I l 2 i. 00CM, Ferini-2 2.0-33 2673W/0051W, 05/24/84 _,.--..__..__m__..__._,.

l TABLE 2.2-4 INHALATION DOSE FACTORS FOR ADULTS * ( EEM PER PCI INHALED) ) Page 1 of 3 eeuCL101., 00NE LIvfa T.8007 THYROIO A10NEY LUNG SI-LLI .... ~. ~.... N 3 NO DATA 1 50C-07 1 50F-07 1.SSE-C7 1.SSE-07 l.SSE-07 1.58E-07 C 14 2 27E-C6 4.26E-07 4.26E-07 4.26E-07 4.26E-07 4.26E-07 4.26E-07 4A 24 1 20E-06 8 28E-06 1 28E-06 1 2SE-06 1.28E-06 1 20E-06 1 20E-36 P 32 1.65E-04 9 64E-06 6.26E-06 NO DATA NC OATA kn DATA 1 00E-05 CR 51 NO DATA NO DATA 1 25 E-0 8 7.44E-09 2.95E-09 1 80E-06 4.15E-07 NN 54 NO DATA 4.96E-06 T. 8 T E-O T NO DATA 3 23E-06 3 75E-04 9.67E-06 NN 56 NU OATA 1 55E-10 2 29E-11 40 DATA 3.63E-30 1 18E-06 2.53E-06 FE 55 3.0TE-06 2.12E-06 4.91E-07 NO DATA NO DATA 9.01E-06 7.54E-07 FE 59 1 47E-06 3.47E-Oe 3 32E-06 40 OATA NO DATA 1 27E-04 2.35E-05 CO 58 40 DATA 1 9tE-07 2 59E-07 NO CATA NC OATA 1 16E-04 1.33E-05 CO 40 NO DATA 1.44E-06 1 85E-06 40 DATA NO DATA 7.46E-04 3.56E-05 MI 63 5.40E-05 3.93E-06 1 01E-06 40 DATA NO DATA 2.23E-05 1 67E-06 11 65 1.92E-10 2 62E-11 1 14F-11 NO DATA N0 DATA 7.00E-07 3.54E-06 CU 64 NO DATA 1.83E-10 T.69E-11 NO DATA ).78E-10 9.4BE-07 6.12E-06 2N 65 4.0SE-06 1 29E-05 9.82E-06 NO DATA O.62E-06 1 00E-04 6.6tE-06 24 69 4.23E-12 8 14E-12 5.65E-13 NO DATA 5.27E-12 1 15E-07 2.04E-09 Da 03 NO DATA 40 DATA 3.01E-Os 40 DATA NO DATA NO DATA 2.90E-00 GR 84 NO DATA NO DATA

3. 91 E-O S NO DATA NO DATA NO DATA 2.05E-13 04 8b NO DATA NO DATA
1. 60E-0 9 NO DATA NO DATA NO DATA LT E-24 4t *e NO DATA 1.69E-05 7.3FE-06 NO DATA NO DATA NO DATA 2.00E-04 40 Sb NO DATA 4.34E-08 2.41E-38 NO DATA NO DATA NO DATA 4.18E-19 RS 49 NO DATA 3.20E-08 2.12E-08 NO DATA NO DATA NO DATA 1.16E-21 Sa 49 3.80E-05 NO DATA 1.09E-06 NO DATA NO DATA 1.75E-04 4.3fE-05 54 90 1.24E-02 40 DATA 7.62E-04 NO DATA NO DATA 1.20E-03 9.02E-05 SR 91 7.74E-09 NO DATA 3.13E-10 NO DATA NO DATA 4.56E-06 2 39E-05 SR 92 8.43E-In NO DATA 3.64E-11 NO DATA 40 DATA 2.06E-06 5 38E-06 Y 90 2.61E-07 NO DATA 7.01 E-0 9 NO DATA 40 DAT A 2.12E-05 6.3IE-05 V 91M 3.26E-11 NO DATA
1. 2 T E-12 NO DATA NO DATA 2.40E-07 1 66E-10 t

V 91 5.78E-05 NO DATA

1. 55 E -06 40 OATA NO DATA 2.13E-04 4.01E-05 Y 92 3.29E-09 NO DATA 3.77E-11 NO DATA
  1. 0 DATA 1 96E-06 9.19E-06 l

i Reference 3, Table E-7. ) 2.0-34 ODCN, Fermi-2 2673W/0051W, 05/24/84 .-~ -. -

TABLE 2.2-4 CONT'D INHALATION DOSE FACTORS FOR ADULTS * (204 PER PCI INHALED) Page 2 of 3 1 aivCLt36 SONE LEVER f.003v TN9A010 alessEt tuses St-LLI V 93 1 18E-08 NO DATA S.26E-10 40 SATA NO Data 6.04E-04 S.27E-05 4 4 IR 95 1 34E-05 4.3CE-06 2 91E-06 NO DATA 4.77E-06 2 2tE-04 8 88E-05 24 97 1 21E-08 2.4SE-09 1 13E-09 NO DATA 3 7tE-09 9.84E-06 6.54E-05 I NS 95 1 76E-06 9.77E-07 S.26E-07 NO pa7A 9 6?f-07 6.3tt-OS 1 30E-OS m0 99 NO DATA I.SIE-OS 2.87E-09 40 DATA 3 64E-04 1.14E-05 3.10E-05 fC 99m 1 29E-13 3.64E-13 4.63E-12 40 Oafa S.52E-12 9.SSE-08 S.20E-07 fC101 S.22E-15 7.52E-15

7. 3 tE -14 40 OATA 1 3SE-13 4.99E-08 f.36E-21 i

aut03 1 9tE-07 NO DafA 8.2 AE -0 8 NO DATA 7.29E-07 6.31E-05 1 30E-05 autos 9 88E-11 NO 0&TA 3 89E-11 NO Data I.27E-10 1.17E-06 6.02E-06 i 1 tul06 8.64E-06 NO DATA 1.0 DE-04 40 04f4 1 67E-05 1.17E-03 1 14E-04 1 4Gl107 1 3SE-06 1.2SE-06 7.4 AC-0 7 40 DafA 2 46E-06 S.79E-04 3 78E-05 IEllSM 4 27E-07 8 98E-07 S. 84 E-0 8 1.3tt-07 1.SSE-06 3.92E-05 0.03E-06 j TE127P 1 58E-04 7.21E-07

1. 9et-0 7 4.11E-07 S.72E-06 1.20E-04 1 87E-05 TEt27 1 75E-10 0 03E-Ll 3 8 7E-11 1 32E-10 6.37E-10 8.14E-07 7 17E-06 IE129* 1 22E-06 S.64E-07 1 98 E-0 7 4.30E-07 4.57E-06 1 4SE-04 4479E-OS 3
  • EI29 6 22E-12 2 99E-12 1.SSE-12 4.87E-12 2 34E-!!

2.42E-07 1 96E-08 i 1E131M 8.74E-09 S. 4 SE- 09 3.63F-09 6.88E-09 3 46E-08 1 82E-05 6.95E-05 fE131 1 39E-12 7.44E-13 4.49E-13 t.17E-12 S.46E-12 1.74E-07 2.30E-09 TEl32 3.2SE-08 2.69E-00 2.02E-08 2.37E-08 1.02E-07 3.60E-05 6.37E-05 I 130 S.72E-07 1 68E-06

6. 60E-0 7 1.42E-04 2.6tE-06 NO Data 9.6tE-07 j

1 131 3.tSE-06 4.47E-06 2.56E-06 1.49E-03 7.66E-06 NO DATA 7.SSE-07 j 1 I 132 1 45E-07 4 07E-07 8.4bE-07 1.43E-05 6 48E-07 NO cafa S.08F-08 l i I 133 1 08E-06 1 8SE-06 S.6SE-07 2.69E-04 3.23E-06 NO Dafa 1.ttf-06 1 134 8.0SE-08 2 16E-07 7.69E-08 3.73E-06 3.44E-07 NO Data 1.26E-10 t 135 3.3SE-C7 8.73E-07 3.2tE-07 5.e0E-05 1.39E-06 NO pata 6.S6E-07 I CSl34 4.66E-OS 1.06E-04 9.10E-05 ho Cafa 3 59E-05 1.22E-05 1.30E-06 CS136 4.88E-06 8 83E-OS

1. 38 E -0 5 40 047a 1 07E-05 1.10E-06 1.46E-06 l

i 1 cst 37 S.98E-05 7.76E-OS

5. 3 5 E-0 5 NO 047a 2 78E-05 9.40f-06 1.0SE-06 j

CSl38 4.84E-04 7.76E-08 4.0$ E-0 8 40 Defa 6.00E-08 6.07E-09 2.33E-13 S4139 1.17E-10 8.32E-84 3 42E-12 NO SATA 7.78E-l4 4.70E-07 1 12E-07 i 4 3 1 i i l 2.0-35 0004, Fermi-2 2673W/0051W, 05/24/84 4 \\

TABLE 2.2-4 CONT'D INHALATION DOSE FACTORS FOR AOULTS* (MREM PER PCI INHALED) Page 3 of 3 NvColut sont E lvEn 7.su0v Tuva0lo aloNEv tweec st.ttl 64140 4.00E-06 6.13f-09

l. 2 t E -0 7 NO D&TA 2.09E-09 1.59E-04 2.73F=05 44141 1.25E-11 9.41E-15 4.20E-13 NO DATA 8.75E-15 2.42E-07 1 45E-17 R4142 3.29E-12 3 30E-15 2.07E-11 NO DATA 2.86E-15 1.49E-07 1.96E-26 LA140 4.10E-C8 2.17E-08 5.73E-09 N0 DATA No DATA 1 70E-05 5.73E-05 LA142 0.54E-il 3.est-il 9.64E-12 NO DATA NO DATA 7.91E-07 2.64E-07 CE141 2 49E-06 l.69E-06 1.91E-07 N0 DATA 7.83E-07 4.52E-05 8 50E-05 CE143 2 33E-09 1.72E-Os 1.91k-0 9 800 D AT A 7.60E-09 9.97E-06 2.03E-05 CEl44 4.29E-04 1.79E-04
2. 30E-0 5 NO DATA 1 06E-04 9.72E-04 1.02E-04 Pal 43 1 17E-06 4.69E-07 5.30E.08 No 04th 2 70E-07 3.5tE-05 2.50E-05 PR144 3.76E-12 1.56E-12
1. 91 E-13 40 DATA 3.ptt-13 1.27F.-07 2.69E-te 40147 6.S9E-07 7.62E-07 4.56 E-0 8 N0 DATA 4.45E-07 2.76E-05 2.16C-05 W 187 1.06E-09 0.85E-lO 3.10E-10 NO DATA NO DATA 3.63E-06 1.94E-05 NP239 2 97E-00 2 82E-09 1.55E-0 9 aso DATA s.75E-09 4.70t-06 l.49E-05 4

1 J 0004, Femi-2 2.0-36 2673W/0051W, 05/24/84

1 T. k TABLE 2.2-5 INGESTION DOSE FACTORS FOR INFANT

  • j (MREM PER PCI INGESTED)

Page 1 of 3 NUC'L f 0t SONE LIVE 4 T.SDDy THvROIO KIDNtv LUNG GI-LLI M 3 NO DATA 3 08E-07

3. 00 E-0 7 3.08E-07 3.08E-07 3.08E-07 3.08E-07 0 14 2.3fE-05 5.06E-06
5. 06 C-0 6 5.06E-06 5.06E-06 5.06F-06 5.06E-06 NA 24 1 01E-05 1 01E-05 1 0lf-05 1 0lf-05 1 01E-05 1 01E-0) 1 01E-05 P 32 1 70E-03 1 00E-04 6.59E-05 NO DATA NO DATA NO DATA 2 10E-05 CR 51 NO DATA NO DATA 1.41E-08 9.20E-09 2 01E-09 1.79E-08 4.tlE-07 j

MN 54 40 DATA 1 99E-0$ 4.53E-06 NO DATA 4.4tE-06 NO DATA 7.3tE-06 3 I MN 56 NO DATA 8.18E-07 1.4 8 E-0 7 NU OATA 7 03E-07 NO DATA 7.43F-05 J FE 55 1.19E-05 8.18E-06 2.40E-06 NO DATA NO DATA 4.19E-06 1 14E-06 FE 59 3.08E-05 5.A8!-05 2.82E-OS NO DATA NO DATA 1.59E-05 2 57E-05 CO 58 NO DATA 3.60E-06 8.93E-06 NO DATA NO D&7A NO DATA 8 9ft-06 CO 60 NO DAT8 1.08E-05 2.55E-05 NO DATA NC OATA NO DATA 2.5TE-05 NI 63 6.34E-04. 3.92E-05 2.20E-05 40 OATA NO DATA NO CATA 1 95E-06 NI 45 4.70E-06 5 32E-07 2 42E-07 NO DATA NO DATA NO DATA 4.05E-c5 Cu 66 NO DATA 6.09E-07 2.82E-0T NO DATA 1 03E-06 NO DAT A 1 25E-05 2N 65 1 34E-05

6. 's t E- 0 5-
2. 9 t E -0 5 NO DATA 3 06E-05 40 DATA 5.33E-05

{N 61 9.33E-08 1 48E-0T 4 25E-08 NO DATA 6.98E-08 NO DATA 1.378-05 na 83 Nn DATA NO DATA

3. 6 3 E-0 7 NO DATA NO DATA NO DATA LT E-24 6R 8*

40 DATA NO DATA J.82E-07 NO DATA NO DATA NO D AT A LT E-24 et 85 NO CATA NO DATA 1.94E-08 NU 04TA NO DATA NO DATA LT E-24 e6 86 NO OATA 1.70E-04 8.40E-05 N0 DATA NO DATA NO DATA 4 35E-06

  1. 8 88 ND OATA 4.98E-07 2.73E-07 NO DATA NO DATA Nn DATA 4.85F-01 RC 89 NO DATA 2.06E-07 1.9ft-37 NO DATA NO DATA NO DATA 9.74E-08 SR 84 2.5tE-03 NG OATA 7.2DE-05 NO DATA NO DATA NO DATA 5.86E-05 SR 90 1.85E 02 NO DATA 4.78E-03 NO DATA NO DATA NO DATA 2.3tE-04 54 91 S.00E-05 NO DATA I.8tE-06 NO DATA NO DATA NO DATA 5.92E-05 la 92 1 92E.05 NO DATA 7.13E-07 NO DATA NO DATA NO DATA 2.0TE-04 Y 90 8.69E-08 NO DATA 2.3st-09 NO DATA NO DATA NO DATA 1.20E-04 Y gia 8 10E-tc NO DATA 2.76E-Il NO DATA NO DATA NO DATA 2.70E-06 Y 91 1.83E-06 NO DATA 3 0lE-08 NO DATA NO DATA NO DATA 8.10E-05 Y 92 7 65E-09 NO DATA 2.15 E-10 NO DATA NO DATA NO DATA 1.46E-04 Reference 3, Table E-14.

2.0-37 ODCH, Fermi-2 2673W/0051W, 05/24/84

TABLE 2.2-5 CONT'D INGESTION DOSE FACTORS FOR IW ANT * (MREM PER PCI INGESTED) Page 2 of 3 l NUCLIOC DONE liver T.500f TNyacle KIDNEY LUNG GI-LLI Y 93 2.43E-05 NO DATA 4.62 E-10 NO DATA NO DATA NO DATA 1.92E-04 2R 95 2.06E-07 5.02E-08 3.56E-08 NO DATA 5.41E-08 NO D AT A 2.50F-05 IR 97 1.40E-08 2.54E-09 1.16E-09 NO DATA 2 56E-09 NO DATA 1.62E-04 48 95 4 20E-08 1.73E-08 1.03E-08 NO DATA 1 24E-08 No DATA 1 46E-05 NO 99 NO DATA 1.4CE-05 6.63E-06 NO DATA 5.00E-05 NO DATA 1.12E-05 TC 99P 1.92E-09 3 96E-09 5.10E-08 NO DATA 4.26E.08 2.07E-09 1.15E-06 TC101 2.27E-09 2.86E-09 2.83E-08 NO DATA 3.40E-08 1 56E-09 4.86E-07 Rul03 1.48E-06 ND UATA 4.95E-07 90 DATA 3 00E-06 NO DATA 1.80E-05 Rul05 1.36E-07 N3 OATA 4.5BE-05 NO DATA 1 00E.06 Nn DATA 5 4tE-05 Rul06 2.41E-05 NO DATA 3.01 E-3 6 No DATA 2 85E-05 NO DATA 1.83F-04 AGilom 9.96E-07 7.27E-07 4.8tE-07 90 DATA 1 04E-06 NO DATA 3.77E-05 TE125M 2.33E-05 7.79E-06

3. l S E-0 6 7.84E-06 NO DATA NO DATA 1.11E-05 TE127p 5.85E-05 1.94E-05 7.ceE-06 1 69E-05 1.44E-04 No nata 2.36E-05 TE127 1.00E-06 3 35E-0T 2.15E-07 8.14E-07 2 44E-06 NO DATA 2.10E-05 7E129M 1.00E-04 3.43!-05 1.54E-05 3.84E-05 2.50E-04 NO DATA 5.97E-05 TE129 2.84E-07 9.79E-08 6.63E-00 2.30E-07 7.0TE-07 NO DATA 2.27E-05 TEl31*

1.52E-05 6.12E-06 5.05E-06 1.24E-05 4 2tE-05 NO DATA 1.03E-04 TEl31 1.76E-07 6.50E-08 4.94E-08 1.97E-07 4.50E-07 Nn DATA 7.llE-06 TE132 2.08E-05 1.03E-05

9. 6 t E -0 6 1.52E-05 6.44E-05 NO DATA 3.StE-05 I 130 6.00E-06 1.32E-15
5. 3 0E -0 6 1.4BE-03 1 45E-05 NO DATA 2.81E-06 1 131 3.59E-05
4. 2 3E-05 1.44E-05 1.39E-02 4.94E-05 NO DATA 1.5tE-06 I 132 1.66E-06 3.37E-06
1. 2 0E -0 6 1.5BE-04 3.7 6 E-D6 NO DATA 2.73E-06 I 133 1.25E-05 1.82r-05 5.33E-06 3.3tE-01 2.14E-35 NO DATA 3.00E-06 1 134 8.69E-07 1.78E-06 6.33E-0T 4.15E-05 1 99E-06 NO DATA 1.84E-06 I 135 3.64E-06 7 24E-06 2.64E-06 6.49E-04 8 07E-06 NO DATA 2.62E-06 C5134 3.77E-04 7.03E-04 7.10 E-0 5 NO CaTA 1.BlE-04 7.42E-05 1.91E-06 C5136 4.59E-05 1.35E-04 5 04E-05 NO DATA 5.30E-05 1 10E-05 2.05E-06 C5137 5.22E-04 6 11E-04. 4.33E-05 NO Data 1.64E-04 6.64E-05 1 9tE-06 C5tl8 4.BIE-07 7.82E-0F 3.79E-0 7 NO DATA 3 90E-07 6.09E-08 1.25E-06 sal 39 8.8IE-07 5.84E-10 2.55E-08 NO DATA 3 5tE-10 3.54E-te 5.5BE-05 l

0004, Fermi-2 2.0-38 2673W/0051W, 05/24/84

x TABLE 2.2-5 CONT'D INGESTION 00SE FACTORS FOR INFANT * (MREM PER PCI INGESTED) Page 3 of 3 NUCLI I 804f LIVER T.000f TNT 4010 EIONEY LUseC GI-LLI 84140 1.71 E 1.?tE-07 s.alf-06 No DATA %.06E-08 1.05E-07 4.20E-05 94141 4.25E-07 2.91E-10 1.3*E-08 No DATA 1.75E-10 1.77E-10 5.19E-06 84t42 3.04E-07 1 53E-10 9.06E-09 NO DATA S.81E-11 9.26E-Il 7.59E-07 Lat40 2.11E-06 S.32E-09 2 14E-09 NO DATA NO DATA NO DATA 9.77E-05 LA142

1. TOE-09 4.04E-10 9.6FE-11 NO DATA NC OATA NO DATA 6.86E-05 CE141
7. ATE-Os 4.00!-08 5 6SE-09 NO DATA 1 40E-06 NO DATA 2.48E-05 CEt43 1.40E-Ce 9.82E-06 1 17E-04 40 DATA 2.96E-09 NO DATA 5.73E-05 CEt44 2.90E-06 1.22E-06 1 67E-07 40 DATA 4.93E-07 NO DATA 1.7tE-04 Pat 43 0.13E-08 3.c4C-08 4.03E-09 NO DATA 1.13E-08 NO DATA A.29E-05 PRt44 2.74C-10 1.06E-10 1 3BE-tt NO DATA 3.R4L-It NO DATA 4.93E-06 N0147 5.53E-08 5.6BE-08 3.48E-09 NO DATA 2.19E-08 NO DATA 3.60E-05 N 187 9.03C-07 6.28s-07 2.17 E -0 7 40 DATA NO DATA NO DATA 3.69E-05 NP2t9 a.itE-Os 9.93E-10 5.6 t E-t o w oATA 1.9st-09 NO DATA 2.s7E-05 00CN, Fermi-2 2.0-39 2673W/0051W, 05/24/84

TABLE 2.2-6 INGESTION DOSE FACTORS FOR CHILD * (MREM PER PCI INGESTED) Page 1 of 3 Mutt roe-sone tevEt T.nove TNvaoIO mIONEv tvec st.Ltr N 3 NO DATA 2.03E.07

2. 0 st-0 7 2.03E-07 2.03E.07 2.03E-07 2 03E.07 c 14 1 2tE-Os
2. 2E-06
2. 42E.0 6 2.42E-06 2.42E.06 2 42E-oe 2.42E.06 44 24 S.s0E.06 s.s0E-c6 s.scE-06 S.83E-06 S.80E-e6 5.80E-06 S.80E-06 e 32 e.2sE-04 3.s6E-05
3. t :E-0 5 40 DATA NO DATA NO DATA 2.28E-05 CR St NO caTA 40 CATA S. 90E-0 9 4.94E-09 I.35E-09
9. 02 E-09 4.72E-07 NN 54 40 DATA 1 0TE-05
2. 8 SE-0 6 NO DATA 3 00C-06 NO DATA 8.90E-06 MN $6 NO DATA 3.34E-OF 7.54E-Os NO DATA 4.04E-07 NO DATA 4.84E-05 FE SS 1 1SE-0$ 6.10E-06 1.895-06 NO DATA NC OAT A 3.4SE-06 1.13E-06 FE 59 1.6st-05 2 67E-05 1 35E-05 40 OATA NO DATA 7.74E-06 2.78E.05 CD Se 40 DATA 1 80E-06
5. S t E-0 6 MO DATA NC OATA NO DATA 1.0SE-0$

CD 60 do DATA S.29F-06 1.56E-05 NO DATA 40 DATA NO DATA 2.93E-05 41 63 5.30E-04 2.88f-05 1.83E-05 NO DATA NO DATA NO DATA t.94E-06 NI 65 2 22E-06 2.09F-07 1.22E-07 NO DATA NO DATA NO DATA 2.56E-05 CU 64 NO OATA 2.45E-07 3 4tE-07 NO DaT4 S.92E-07 40 DATA I.15E-OS 2N 65 1.37E-05 3.6SE-03 2.2TE-OS NO DATA 2.30E-05 NO DATA 6.4tE-06 IN 69 4.38E-08 6.43E-OS S.tSE-09 NO DATA 3.84E-05 NO DATA 3.99E=06 em SJ NO DATA NO DATA 1.7tE-07 NO DATA NO DATA NO DATA LT E-24 SA 84 N0 DATA NO DATA 1.9 9d-0 7 NO DATA NO DATA NO DATA LT E-24 AR 8) NO DATA NO DATA 9.12E-39 NO DATA NC OATA NO DATA LT E-24 as 06 NO DATA 6.70E-05 4.12E-05 NO DATA NO DATA NO DATA 4.3tF-06 28 88 NO DATA t.90E-07 8.32E-37 NO DATA NO Dafa NO DATA 9.32E-09 At 89 NO DATA 1.17E-07 1.04E-07 40 Data NO Data NO DATA t.02E-09 i la 39 a.32E-03 NU CATA 3.7 T E-0 5 NO DATA 40 DATA ND UaTA S.11E-05 SR 90 1.70E-02 40 UATA

4. 3 t E-0 3 f40 DaT A N0 DsTA 40 Dafa 2.29E.c4 SR 91 2.40E-05 NO DATA 9.06E-07 NO DAfa NO DAfa NO DATA S.30E-05 SR 92 9.03E-C6 40 D AT A 3.62E-07 NO DATA NO DATA NO DATA t.7tE-04 Y 90 4.!!E-08 NO DATA 3.10E-09 NO DATA NC Data No DATA 1.ifE-04 Y 9tM 3.82E-10 NO DATA t.31E-11 ho DATA 40 DATA Nn DATA F.4sf.c7 Y 91 6.02E-07 40 DATA 1.6 t E.0 0 40 DATA NO DATA NO DATA 8.02E-05 i

V 92 3.60E-09 40 DATA 1.0 AE-10 N0 DATA NO DATA NO 0414 t.04E.04 1 i l l l Reference 3, Table E-13. 2.0-40 0D04, Fermi-2 2673W/0051W, 05/24/84

TABLE 2.2-6 CONT'D INGESTION DOSE FACTORS FOR CHILDS (MEM PER PCI INGESTED) Page 2 of 3 seuCL IOE 00seg LivEt T.000t TNVROIO ElthEY LueeG GI-LLI V 93 I.34E-OS NO DATA 3.13E-10 NO DATA NO DATA NO DATA 1.70E-04 2R 95 1.16E-07 2 35E-08 2.27E-08 NO DATA 3.65E-08 NO DATA 2.66E-05 le 97 6.99E-09 1.01E-09 b.96E-10 No DATA 1.45L-09 NO DATA 1.53E-04 NB 95 2 25E-08 8.76E-09 6.26E-09 40 OAT A 8.23E-09 NO DATA 1 62E-05 MO 99 NO DATA I.33E-05 3.29E-06 NO DATA 2.84E-05 NO DATA 1.10E-05 TC 998 9.23E-10 1.81E-09 3.00E-Os NO DATA 2 63E-08 9.19E-10 1.03E-06 FC101 1 07E-09 1 126-09 1.42E-08 NO DATA 1.91E-08 5 92E-10 3.56E-09 Rut 03 7.31E-07 NO DATA 2.etE-07 NO DATA 1 84E-06 NO DATA t.89E-05 AU105 6.45E-08 NO DATA 2.34E-06 NO DATA 5.67E-07 No DATA 4.21E-05 t Rut 06 1.17E-05 NO DATA 1 46E-06 NO DATA 1.50E-05 NO DATA 1.02E-04 A0!!0M 5.39E-07 3.e4E-07 2.91E-07 NO DATA 6.78E-07 NO DATA 4.33E-05 IE125M 3.14E-05 3.09E-06

1. 52 E-0 6 3.20E-06 NO DATA NO DATA 1.10F-05 TE12FM 2.89E-05 7.78E-06 3 4sE-06 4.91E-06 f.24E-05 NO DATA 2.34E-05 TE127 4.71E-07 1.21F-07 1.01E-0 7 3.26E-07 1.34E-06 NO DATA 1.34E-05 EE129 4.87E-05 1.36E-05 7.5eE-06 1.57E-05 1.43E-04 NO DATA 5 94E-05 fE129 1.34E-07 3.74E-08 3.18E-OS 9.56E-00 3.92E-07 NO DATA 4.34E-06 TElllM 7.20E-06 2.492-06 2.65E-06 5.12E-06 2.41E-05 NO DATA 1.01E-04 TE131 0.30E-08 2.531-00 2.47E-00 6.35E-06 2.51E-07 NO DATA 4.36E-07 TE132 1.01E-05 4.47E-Oe 5.40E-06
6. Sit-06 4.15E-05 NO DATA 4.50E-05 i 130 2.92E-06 5.90E-06
3. 04 E-0 6 6.50E-04 8.82E-06 NO DATA 2.76E-06 i

I 131 1.72E-05 1.73E-05

9. 8 J E-0 6 5.72E-03 2.84E-05 No DATA 1.54E-06 I 132 8.00E-07 1.47E-06 e.76E-07 6.82E-05 2.25E-06 NO DAT A 1.73E-06 3 133 5.92E-06
7. 'J 2 E - 06 2.7 7 E-0 6 1 36E-03 1.22E-05 NO DATA 2.95E-06 8 134 4.19E-07 7.7sE-07 3.5BE-07 1.79E-05 1.19E-06 NO DAT A 5.16E-07 I 135 1.75E-06 3.15E-Oe 1.49E-06 2 79E-04 4.83E-06 NO DATA 2.40E-06 C1134 2.34E-04 3.84E-04 8.10E-05 NO DATA 1.19E-04 4.27E-05 2.07E-06 C1136 2.35E-05 6.46E-05 4.10E-0 5 NO DATA 3.44E-05 5.13E-06 2.27E-06 C5837 3.27E-04 3.13E-04
4. 62 E-0 5 NO DATA 1.02L-04 3.67E-05 1.96E-06 C1138 2.20E-07 3.17E-07
2. 0l f -0 7 NO DATA 2.23E-07 2.40E-OS 1.46E-07 san 39 4.14E-07 2.21E-10
1. 20E -O s NO DATA 1.93t-10 1.30E-10 2.3*E-05 i

00m, Femi-2 2.0-41 2673W/0051W, 05/24/84

T TABLE 2.2-6 CONT'D INGESTION 00SE FACTORS FOR CHILO* (MREM PER PCI INGESTED) Page 3 of 3 auCLlut DowE t t vEa - f.ao0e invao!O at0 NET tvNo st-Ltt ..................s........... a4:40 e.stE-05 7.28E-08

4. 85E-s e NO Data 2.37t-08 4.34E-08 4.21E-05 34141 2 00E-07 1.12E-10
6. bl E-0 9 NO DATA 9.69E.11 4.58E-10 1.14E-07 04142 8.74E-08 6.29E-11
4. 8 8 E-0 9 NO DATA 5.09E-11 3.70E-11 1 14E-09 L4140 1 0tt-08
3. 5 3E-09 1.19E-0 9 40 DATA NO OATA NO DATA 9.84E-05 Lat42 5.24E-10 1.67E-10 S.21E-11 NO DATA NO D A T 4 NO DATA 3.31E-05 CEt41

).97E-0A 1.90E-08 2 94E-0 9 NO DATA 8.68E-09 NO DATA 2.47E-05 ) CE14J 6.99E-09 3.79E-06 5.49E-10 NO DATA 1.59E-09 NO DATA 5.55E-05 CE144 2.08E-06 6.52E-07 1.IIE-07 NO DATA 3.61k-07 NO DATA 1.70E-04 Pal 4 3 3.93E-08 1.18E-08 1.95E-09 40 DATA 6.19E-09 NO DATA 4.24E-05 Patte 1.29E-10 1.97E-!! 6.49E-12 NO DATA 2.llE-11 NO DATA 8.59E-08 NCl47 2.79E-0A 2.26E-08 1.75E-09 NO DATA 1.24E-04 NO DATA 3.58E-05 W 187 4.29E-07 2.54f-07 1.14E-07 NU Data NO DATA NO 04T4 3.57E-05 NP239 5.2bE-09 3.77E-10 2.6M-10 een DAT A 1.09E-09 WO DATA 2.79E-05 t i i i 1 i i a W I i 1 l i .i 00CN, Fermi-2 2.0-42 2673W/0051W, 05/24/84

TABLE 2.2-7 INGESTION DOSE FACTORS FOR TEENAGER # ( EEM PER PCI INGESTED) Page 1 of 3 \\ seUCLICE SONE L t9Et E.00ET TNvaels st0 NET LUseG St.LLI i H 3***40 DATA 1.06E-07 1 0ef-0 7 1 04E-07 1 04E-07 L.06E-07 1 06E-07 4 C 34 4.06E-06 8.12E-07 8.12 E-0 7 8.12F-07 8.12E-07 8.12E-07 8 12F 4A 24 2 50E-06 2.30E-94 2 30E-04 2 30E-06 2.30k-06 2 10E-06 2 30E 4 P 32 2 76E-04 1.71E-OS 4 0?E-05 N0 DATA NO DATA NO DATA 2 32E-09 i Ca SR 40 DATA 40 DATA 3 60E-09 2.00E-09 7.89E-10 S.14E-09 4.0SE-07 i PN S4 40 DATA S.90E-Oe 3 17E-06 40 DATA 1.76E-06 NO DATA 1.21E-09 884 $6 800 DAT A 1.tSE-07

2. 8 t f-0 8 NO DATA 2.00E-07 NO DATA 1.04E-05 FE SS 3 78E-06
2. t,8E-04 6.2 SE-0 7 sen DAT A MC DATA t.70E-06 1 16E-06 FE 19 S.87E-06 1.sTE-OS S.29E-06 NO DATA 40 DATA 4.32E-04 3 26E-06 4

..............NO DATA 1.3*E-05 CO SS 40 DATA 9.72E-07

2. 24 E-0 6 NU OATA NO DATA CU 40 NO DATA 2 8tE-06
6. 3 3E-06 NO DATA 40 DATA NO Data 3.66E-OS est 63 1 77E-04 3.2SE-05 0.00E-06 40 DATA es0 DATA NO DATA 1.99E-06 i

gf 65 7 49E-07 9.b7E-08 4.36E-08 40 DATA 40 DATA NO 04TA S.19E.06 I CU 64 NO D&T4 1.15E-07 S.41E-08 NO DATA 2.91E-07 NO DATA S.92E-06 24 6b S.76E-06 2.COE-ES 9.15E-0 6 800 UAT4 1.28E-05 40 Data 8.47E.06 4 1 goe 69 1 47E-05 2 60E-08 1 96E-0 9 40 DATA 1.a1E-08 esO DATA S.16E-08 j I R4 83 es0 04TA es0 047 A b.74E-08 seO 04TA NO DATA NO DATA LT E-24 1 On 84 000 DATA sen Cafa

7. 2 2 E-0 8 880 DaT A WC DATA NO DATA LT E-24 l

...............800 DAT& es0 04T A LT E-24 na 8% 800 04TA 40 DafA 3 0$t-09 NO 04TA at 86 esO OaTA 2 98E-05 1 40E-05 se0 DATA 40 DATA 40 CATa 4.4tt=06 i y 48 88 NO DATA 8.$2E-0A 4.54E-04 NO DATA se0 04TA NO DATA 7.30E-il j 888 89 880 DAT 4 S.50E-08 3 89E-08 40 DATA NO DATA NO DATA 8 45E-17 l Sa 87 4.40E-04 NO 04Ta 1 26E-05 NO DATA NO DATA N0 0474 9 2*E.05 S4 90 8.30E-03 eso 0414 2 0SE-0 3 NO DATA sen 0414 NO OST A 2.llf-04 SR 98 8.CTE-06 peo 04Ta 3 2 t E-07 40 DaT4 NO DATA NO DATA 3 66E-05 i $4 92 3.0$E-06 NO 04ta 1.30E-07 40 DATA NO DATA NO Dat a 7.7?E-05 i V 90 1.37E-08 es0 CATA 3.67E-10 NO DATA 880 04T A NO DATA 1 13E-04 j l. s / v 91> 1 29E-10 NO DATA 4.93E-12 NO DATA sec OAT A suo CaTA 6.09E.n* I f 91 2 0lf-07 40 CATA S. 39E-0 9 40 DATA NO Data No DATA 8.24E-05 Y 92 1 21E-09 000 Defa 3.SOE.Lt 40 DATA 800 DATA se0 OATA 3 32E-05 7 1 4 4 i I i I 1 1

  • Reference 3, Table E-12.

1 1 i 3 2.0-43 l ODO4, Fermi-2 2673W/0051W, 05/24/84

TABLE 2.2-7 CONT'D INGESTION DOSE FACTORS FOR TEENAGERO (W404 PER PCI INGESTED) Pege 2 of 3 P muttlag 00=8 tivte 7 000v 7:090010 alente tv=s sl.tti ... ~..... ...... -..... _........ ~.... v 93. 3 03t-e9 90 esta a.est.10 me Data see Saf a soo Data 1.t?t.04 te 95 4.328-00 1.30C-00 0.944 09 es0 Safe 3 916-04 8e0 04f A 3 006-09 l 2 378-99 4.09t-LO 2.166-10 40 SATA 7.818 40 000 04T4 1 276-04 to 97 est 95 0.228-99 4.561-09 2.llt=09 100 SAT A 4.421 04 ase DATA 1.95t-09 sec 99 te0 Safa 6.03C.06 1 166-06 se0 04f4 8 58t.09 ese 04fA l.08t-09 EC 99m 3 128-10 9.26t-80 3.20t-08 Is0 041& L.let.08 S.44E-10 4.006-07 .............................3.12E.10 8.798-17 TCitt 3.60E-10 9.124-10

9. 03 t-0 9 con 041a 9.268-09 0U803 2.998-07 ese Date 1.098-07 8e0 Data s.995 07 son Data 2 13E.09 SWl99 2 888-04 NO 04f4 0 465-09 see Safa 2.798-07 NO DATA 1 741-09 Sulee 3 924 04 se0 DATA 4.948 07 se0 DATA 7.968-04 NO DATA 1 808-04 asl10* 2 058-07 l.948 07 8 831 07 8ec Safa 3.70E-07 8p0 Defa 9 45t-05 fil2Dn 3.838-04 8 388 06 S.824-07 1 07t-@6 ese Safe 40 SafA l.13t=05

........................................................... ~.. -. TEl27m 9.678 06 3.4 st.06

1. l bt-0 4 2 30t= 06 1 926-05 800 Daf e 2 488-0S V8827 8 588-07 5.60E-04 3 40E-08 1 094-07 6.404-07 000 0474 1.22E.0S fil29M l.63E-OS 6.CSF-86 2.let-06 S.26t-06 6.428-05 kn Safa 6.128 0S 78829 4.488-06 3 67t-04 1.098-00' 3 204 08 1 00t=07 40 DATA 2 4%f-81 filst* 2 448 06 1 11C-06 9.76t-07 1.76t 06 1 228-05 40 Defe 9 39t=0S TE131 2 798 00 1.lSt-00 e.12t-04 2 198-08 1 228-07 NO Defa 2 29C-09 fil32 3 498 06 2.21E-04 2 061-06 2.338-06 2 12t*06 40 Dat a 7.006-09 4 130 3 038-06 2 908-C6 1 19t-06 2 41t=04 4.59t-06 ho DATA 2 29t-06 I lll 5 018-04 8.19C-06 4.40E-06 2.394-03 1 488-05 20 Data 1 42t=04 I ISP 2 79t-07 7.308 07 2.624-07 2 46t-09 1 194 04 NO DAT A 3.188-07 1 133 2 01E-06 1.41k-06 1.044 06 4.76t-04 5.944 06 NO Date 2.198 06

,8 134 1 44E-07 3 878 07 1 39t-07 6.498-06 6.108-07 sec Def a 9 108-99 8 13% 6.10t-07 1 578 06 S.82E-07 1.0lt.04 2.404-06 NO Data 1.748 06 Clite 8.37E-06 1 97t 04 9.168 0$ NO D&fa 4.268-OS 2.398-05 2.45t-06 Cll36 8.$98-06 3.Aet 05 2.27t-Dt NO DATA l.844-05 2 908-06 2 728 06 C1837 1 128 04 1.49t=04 S.191-0 S NO Defa 9.078-0S 1 9ft-0$ 2.Itt-04 Cll30 7.768 08 8 498-07 7.468-08 h6 0414 8.let-07 1 26t 04 6.76E-ll Sal 39 8 39t-07 e.2st.ll 4.0bt.09 no esta 9.22t-il e.74t-ll 1.24t-06 l 2.0 44 / 00CN, Fermi-2 1 2673W/0051W, 05/24/84 i

TABLE 2.2-7 CONT'D INGESTION DOSE FACTORS FOR TEENAGER 0 (MREM PER PCI INGESTED) Page 3 of 3 w Ctsis some teven t.coor twyto 0 ste=tv toss st.tt! sa140 2.s4t.03 3.4nt-Os i.e st-e 6 wo eatA

t. net.oo 2 54t-ce
4. set.es i

84141 6.71E-OS 5.ntt-il

2. 2 4 t-0 9 40 DATA 4.6SE-11 3 43t=88 8.43t-83 84142 2 99C-00 2 99E-18 1 045-09 40 OATA 2.53t-11 1 99t-11 9.let-20 Lat40 3 441-09 1.ftt-09 4.ll -10 NO Data hc OATA NO 04f4 9.02t-0$

14842 8 79E-10 7.91t-11

1. 90t =11 40 DATA 40 DATA h0 DATA 2.42t-06 C6141 1 35t-08 0.98t-09
1. 02 E-0 9 40 DATA 4.101-09 NO 04f4 2.54t=0S Cale) 2 3St=09 1 7tt-06
1. 91 t-10 h0 04fA 7.67t-10 NO DATA S.14t=0S Ct144 6 96t-07 2 00t-07 3.74t -0 6 NO Defa 1 72E.07 40 DATA
1. T S F.04 Pat 4) 1 31E-04 S.23C-09 6.S21-10 hu OAT 4 3 641-09 h0 CATA 4.31t=0S PAlen 4.33E-11 1.76t-11 2.10t-12 NO Data 1.0tt.11 ho DATA 4.74t-14 40147 9.18C-09 1.02F-04 6.Ilt-10 40 DefA S.99E-09 kn 04TA 3.60s-05 h 107 8 46t=07 8.19t-07 4 178-08 40 DafA 40 04fA NO Defa 3.22t-05 ge239 a.16t.09 1.66t-te 9.22t-11 he oata S.2tt.10 No eafA 2 61t.Os 00C'1, Fermi-2 2.0-45 2673W/0051W, 05/24/84

TABLE 2.2-8 INGESTION DOSE FACTORS FOR ADULTS * (MREM PER PCI INGESTED) Page 1 of 3 muc 899E tivER T.sDcv TNvRD:D alDNEv LuMc ci-tt! .. L,1 cE.. H 3 NO DATA 1.05E-07

1. 05 E -0 7 1.05E-07 1.05E-07 1 05E-07 1.05E-07 C 14 2.8AE-06 5.68E-07 5.68E-07 5 68E-07 5.68E-07 5.68F-07 5.68E-07 NA 24 1.70E-06 1.70E-06 1 70E-06 1.70E-06 1.70E-06 1 70E-06 1 70E-06 P 32 1.93E-04 1.20E-05
7. 4 6 E-0 6 NO DATA NC DATA NO DATA 2.17E-05 CR 51 NO DATA 40 CATA 2.60E-09 1 59E-09 5.86E-10 3.53E-09 6.69E-07 NN 54 ND DATA 4.575-06 8.72E-07 NO DATA 1.36E-06 NO DATA 1.40E-05 NN 56 NO DATA 1.155-07 2 04E-0 4 NO DATA 1 46E-07 NO DATA 3.67E-06 rE 55 2.75E-06 1.90F-06 4.4 JE-0 7 NO DATA NO DATA 1.06E-06 1.09E-06 FE 59 4.34E-06 1.02E-05
3. 91 E-0 6 NO DATA NO DATA 2.85E-06 3.40E-05 CD 58 NO DATA 7.456-07 1.67E-06 40 DATA NO DATA NO DATA 1 51E-05 CO 60 NO DATA 2.14f=06 4.72E-06 NO DATA NO DATA NO DATA 4.02E-05 MI 63 1.30E-C4 9.01E-06 4.36E-06 NO DATA NO DATA NO DATA 1 88E-06 NI ob 5.28E-07 6.86E-08 3.13E-08 NO DATA NO DATA NO DATA 1 74E-06 CU 64 NO DATA 8.33E-08 3.91E-OS NO DATA 2.10E-07 NO DATA 7.10E-06 2N 65 4.84E-06 1.54E-05
6. 9eE -0 6 NO DATA 1.03E-05 NO DATA 9.70E-06 2N 69 1.03E-08 1 17E-08 1.37E-09 NO DATA 1.28E-03 No DATA 2 96E-09 BR 83 NO DATA NO DATA 4.02E-08 NO DATA NO DATA NO DATA 5.79E-08 SR 84 NO GATA NO DATA 5.21E-08 NO DATA NO DATA NO DATA 4.09E-13 BR 85 NO DATA NO DATA 2.14 E-0 9 NO DATA NO DATA NO DATA LT E-24 48 86 NO DATA 2.11E-05
9. 8 3 E-0 6 NO DATA NO DATA NO D AT A 4.16E-06 RB 88 NO DATA 6 051-08 1.21E-08 NO DATA NO DATA NO DATA 8.36E-19 RB 89 NO DATA 4.01E-08 2.82E-08 id) DATA NO DATA NO DATA 2.33E-21 SR 89 3.08E-04 NO DATA
8. 84 E-0 6 NO DATA NO DATA NO DATA 4.94E-05 SR 90 7.58E-03 NO DATA 1.86E-03 NO DATA NO DATA NO DATA 2.19E-04 SR 91 5.6TE-06 NO DATA 2.29E-07 40 DATA NC DATA NO DATA 2.70E-05 5R 92 2.15E-06 NO DATA 9.30E-08 NO DATA NC DATA NO DATA 4.26E-05 y 90 9.62E-09 NO D,ATA
2. 5 8 E -10 NO DATA NO DATA NO DATA 1.02E-04 v 91M 9.09E-11 NO DATA 3.5 2 E-12 NO DATA NO DATA NO DATA 2.67E-10 Y 91
1. 41 E-0.7 40 DATA 3.77E-09 NO DATA NO DATA NO DATA 7.76E-05 Y 92 8.45E-10 WO DATA 2.47E-11 NO DATA NO DATA NO DATA 1.48E-05 s

Reference 3, Table E-11. 0004, Fermi-2 2.0-46 2673W/0051W, 05/24/84 l MM n - -. _ .c m, s

TABLE 2.2-8 CONT'D INGESTION DOSE FACTORS FOR ADULTS * (MREM PER PCI INGESTED) Page 2 of 3 E '1 NUCL10J-SONE LIVER 7.800T 7N74010 E10NEY LUNG St-LL1 l V 93 2.60E-C9 NO DATA 7.40E-11 NO DATA NO DATA NO DATA 8.50E-05 2R 95 3.04E-08 9.75E-09 6 60E-09' NO DATA 1.53E-05 NO DATA 3.09E-05 2A 97 1.68E-09 3 392-10.1 55E-10 NO DATA 5 12E-10 NO DATA 1.05E-04 M8 95 6 22E-09 3 46E-09

1. 86E-0 9 NO DATA 3.42E-09 NO DATA 2.10E-05 ND 99 NO DATA 4.31E-06 8.20E-0 7 NO DATA 9.76E-06 NO DATA 9.99E-06 TC 99M 2.47E-10 6.98E-10
8. 89 E-09 NO DATA 1 06E-08 3.42E-10 4.13E-07 l'

TC101 2.54E-10 3 66E-10

3. 59E-0 9 NO DATA 6.59E-09 1.87E-10 1.10E-21 4U103 1 85E-07 MO DATA 7.9FE-08 ND DATA 7.06E-07 NO DATA 2.16E-05 RU10b 1.54E-08 NU CATA 6.00E-09 NO DATA 1 99E-07 NO DATA 9.42E-06 1

AU106 2.75E-06 NO DATA 3.4 sE-07 NO 04T A 5.31E-06 NO DATA 1.78E-04 ) Action 1 60E-07 1 40E-07 8.79E-08 NO DATA 2.91E-07 NO DATA 6.04E-05 TE125M 2.6SE-06 9.71E-07 3.59E-07 8 06E-07 1 09E-05 NO DATA 1.07E-05 TE127* 6.77E-06 2.42E-06

8. 25 E-0 7 1.73E-06 2.75E-05 NO DATA 2.27E-05 TE127 1.10E-07 3 95E-08 2.38 E-0 8 8.15E-05 4.48E-07 NO DATA 8.68E-06 TE129M 1.15E-05 4.29f-06 1 82E-06 3.95E-06 4.00E-05 NO DATA 5.79E-C5

...........................~........................................... l TE129 3.14E-08 1 18E-08 7.62E-09 2.41E-08 1.32E-07 NO DATA 2 37E-Os TE131m 1.73E-06 8.46E-07 7.05 E-0 7 1.34E-06 8.57E-06 NO DATA 8.40E-05 TE131 1.97E-Os 8.23E-09 6.22 E-0 9 1.62E-08 8.63E-08 NO DATA 2.79E-09 I TE132 2.52E-06 1 6)E-06 1.5)E-06 1.00E-06 1457E-05 NO DATA 7.71E-05 l 1 130 7.56E-07 2.21E-06 8.80E-07 1.89E-04 3.4SE-06 NO DATA 1.92E-06 1 131 4.16E-06 S.95E-06

3. 41E-0 6 1.95E-03 1.02E-05 NO DATA 1.57E-06 l

1 132 2.03E-07 5.43E-07 1.90E-07 1.90E-05 8.65L-07 NO DATA 1.02E-07 ? 1 133 1.42E-06 2.4TE-06 7.53 E-0 7 3.63E-04 4.31E-06 NO DATA 2.22E-06 1 1 134 1.06E-07 2.08E-07 1.03E-LT 4.99E-06 4.5sE-07 NO DATA 2.51E-10 l'135 4.43E-07 1.16E-06 4.2 8E-0 7 7.65E-05 1.86E-06 NO DATA 1.31E-06 C5134 6.22E-05 1.48E-04 1.21 E-0 4 NO DATA 4.79E-05 1.59E-05 2.59E-06 -j C5136 6,51E-06 2.57E-05

1. 05 E-0 5 NO DATA 1.43E-05 1.96E-06 2.92E-06 i

CS137 7.97E-05 1.09E-04 7.14E-0 5 NO DATA 3.70E-05 1.23E-05 2.11E-06 C5138 5.52E-08 1.09E 5.40E-08 NO DATA S.01E-08 7.91E-09 4.65E-13 SA139 9.70E-08.6.91E-11 2.84E-49 NO DATA 6.46E-11 3 92E-11 1.72E-07 t i 1, i a J I n d I i ODW, Fermi-2 2.0-47 2673W/0051W, 05/24/84 1 a-. ..--..--.y .--.y .-,-,,-c- ,w-.--y,-.,w__,,, ,,m-. c,,,

TABLE 2.2-8 CONT'D 1 INGESTION DOSE FACTORS FOR ADULTS * (MREM PER PCI INGESTED) Page 3 of 3 wctics... sone Livfa r.acor 7Nye01o stoney LvNc sr-LEr i 1 sA140 2.Ost-05 2.55E-Os 1.ssf-os No DATA s.6Tv-09 1.46E-Os 4.tef-05 I R4141 4.T1E-08 1.56E-11 1 59E-09 40 DATA 3 31E-11 2.02E-11 2 22E.l? j 2 13E-08 2.19E-11 1 34E-09 NO DATA 1 85E-11 1.24E-11 1.00E-26 ,94142 LA140 2.>0E-09 1.262-09 J.33E-10 NU OATA NO DATA NO DATA 9.25E-05 LA142 1.28E-10 5 82E-11 1 45E-11 NO DATA NG DATA NO DATA 4.25E-07 CE141 9.36E-09 6.33E-09 T.18C-10 NO DATA 2 94E-09 NO DATA 2 42E-05 i i CE143 1.65E-09 1 22E-06

1. 35 E-10 NO DATA 5.37E-10 NO DATA 4.56E-05 CE144 4.ASE-07 2.04E-07 2.62E.08 NO DATA 1 21E-07 NO DATA 1 65E-04 P4143 9.20E-09 3 69E-09 4.56E-10 NO DATA 2.13E-09 NO DATA 4.03E-05 i

P4144 3.01E-11 1.25E-11 1.56E-12 NO DATA 7.05E-12 NO DATA 4.33E-18 N0147 6.29E-09 7.27E-09 4.35E-10 NO DATA 4.25E-09 40 DATA 3 49E-05 i N 19F 1.03E-07 8.61E-08 3.01 E-0 8 NO DATA NO DATA NO DATA 2 82E-05 I Nr239 1.19E-09 1.17E-10 e.4 5E-11 NO DATA 3.65E-10 NO DATA 2 40E-05 J 1 4 j 1 i k l i 1 2.0-48 ODCM, Fermi-2 2673W/0051W, 05/24/84 ~.

TABLE 2.2-9 EXTERNAL DOSE FACTORS FOR STANDING ON CONTAMINATE 0 GROUN0* 2 (mrem /hr per pci/m ) ELEMENT TOTAL BODY SKIN H-3 0.0 0.0 p.-14 0.0 0.0 NA-24 2.50E-08 2.90E-08 P-32 0.0 0.0 Cr-51 2.20E-10 2.60E-10 Mn-54 5.80E-09 6.80E-09 Mn-56 1.10E-08 1.30E-08 Fe-55 0.0 0.0 Fe-59 8.00E-09 9.40E-09 Co-58 7.00E-09 8.20E-09 Co-60 1.70E-08 2.00E-08 Ni-63 0.0 0.0 Ni-65 3.70E-09 4.30E-09 Cu-64

1. 50E-09 1.70E-09 Zn-65 4.00E-09 4.60E-09 Zn-69 0.0 0.0 Br-83 6.40E-11 9.30E-ll Br-84 1.20E-08 1.40E-08 Br-85 0.0 0.0 Rb-86 6.30E-10 7.20E-10 Rb-88 3.50E-09 4.00E-09 Rb-89 1.50E-08 1.80E-08 Sr-89 5.60E-13 6.50E-13 Sr-91 7.10E-09 8.30E-09 Sr-92 9.00E-09 1.00E-08 Y-90 2.20E-12 2.60E-12 Y-91M 3.80E-09 4.40E-09 Y-91 2.40E-ll 2.70E-11 Y-92 1.60E-09 1.90E-09 Y-93 5.70E-10 7.80E-10 Zr-95 5.00E-09 5.80E-09 Zr-97 5.50E-09 6.40E-09 Nb-95 5.10E-09 6.00E-09 Mo-99 1.90E-09 2.20E-09 Tc-99M 9.60E-10 1.10E-09 Tc-101 2.70E-09 3.00E-09 Ru-103 3.60E-09 4.20E-09 Ru-105 4.50E-09 5.10E-09 Ru-106 1.50E-09 1.80E-09 Ag-110M 1.80E-08 2.10E-08 Te-125M 3.50E-11 4.80E-11 Te-127M 1.10E-12 1.30E-12 Te-127 1.00E-11 1.10E-ll Te-129M 7.70E-10 9.00E-10 Te-129 7.10E-10 8.40E-10
  • Reference 3, Table E-6 ODCM, Fermi-2 2.0-49 2673W/0051W, 05/24/84

TABLE 2.2-9 (Continued) ELEMENT TOTAL BODY SKIN Te-131M 8.40E-09 9.90E-09 Te-131 2.20E-09 2.60E-06 Te-132 1.70E-09 2.00E-09 I-130 1.40E-08 1.70E-08 I.-131 2.80E-09 3.40E-09 I-132 1.70E-08 2.00E-08 I-133 3.70E-09 4.50E-09 I-134 1.60E-08 1.90E-08 I-135 1.20E-08 1.40E-08 Cs-134 1.20E-08 1.40E-08 Cs-136 1.50E-08 1.70E-08 Cs-137 4.20E-09 4.90E-09 Cs-138 2.10E-08 2.40E-08 Ba-139 2.40E-09 2.70E-09 Ba-140 2.10E-09 2.40E-09 Ba-141 4.30E-09 4.90E-09 Ba-142 7.90E-09 9.00E-09 La-140 1.50E-08 1.70E-08 La-142 1.50E-08 1.80E-08 Ce-141 5.50E-10 6.20E-10 Ce-143 2.20E-09 2.50E-09 Ce-144 3.20E-10 3.70E-10 Pr-143 0.0 0.0 Pr-144 2.00E-10 2.30E-10 Nd-147 1.00E-09 1.20E-09. W-187 3.10E-09 3.60E-09 Np-239 9.50E-10 1.10E-0? \\ l 00CM, Fermi-2 2.0-50 2673W/0051W, 05/24/84

TABLE 2.1-1 00SE FACTORS FOR EXPOSURE TO A SENI-IWINITE CLOU0 0F NOBLE GASES

  • Nuclide y-Body *** (K)

B-Skin ***(L) y-Air **(M) 8_-Air ** (N ) Krh5m 1.17E+03**** 1.4E+03 1.23E+03 1.97E403 Kr-85 "'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 1.0E+04 Kr-90 1.56E+04 7.29E+03 1.63E+04 7.83E+03 Xe-131m 9.15E+01 4.76E+02 1.5E+02 1.11E+03 Xe-133m 2.51E+02 9.94E+02 3.27E+02 1.48E+03 Xe-133 2.94E+02 3.0E+02 3.53E+02 1.05E+03 Xe-135m 3.12E+03 7.11E+02 3.3E+03 7.39E+02 Xe-135 1.81E+03 1.8E+03 1.92E+03 2.46E+03 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-41 8.84E+03 2.69E+03 9.30E+03 3.28E+03

  • Values taken from Reference 3, Table B-1
    • mrad-m3 pCi-yr
      • mrem-m3 pCi-yr 3
        • 1.17E+03 = 1.17 x 10 ODCM, Fermi-2 2.0-5 2673W/0051W, 05/24/84

-\\ TABLE 2.1-2 GASEOUS RELEASE PATHWAY FLOW RATES l i Flow Rate (cc/sec)* j Release Pathway 5.1E4 7 1. React 0,r Building Exhaust Plenum 4 (011-N407) 1.9E+6 2. Standby Gas Treatment System (D11-N406A and B) 1.4E+7 3. Radwaste Building Ventilation (D11-N403) 1.5E+7 4. Service Building Ventilation (D11-N405) 1.8E+8 5. Turbine Building Ventilation (D11-N404) 2.5E+6 6. Dnsite Storage Building Ventilation (011-N508) 1 i J Reference 5 4 e 1 l ODCM, Fermi-2 2.0-6 2673W/0051W, 05/24/84 + ,r -n- ,--,_.--,,-,---,,--,,.,,.--,e --n

2.2 GASEOUS EFFLUENT DOSE RATE AND DOSE CALCULATIONS 2.2.1 UMESTRICTED AREA BOUNDARY DOSE RATES 2.2.1.a Dose Rates Due To Noble Gases For the purpose of implementation of STS 3.ll.2.1.a, the dose rate at the unrsstricted area boundary due to noble gases shall be calculated as follows: D = total body dose rate at time of release (mrem / year) t YM (K Q) = g 1 D = skin dose rate at time of release (mrem /yr) 3 X/Q [{(L + 1.1 M ) Q ] = f f f i (NOTE: terms defined previously in Section 2.1.1) In the event of simultaneous releases, dose rates shall be summed to assure that dose rate limits are not exceedad. 2.2.1.b Dose Rates Due to Radiciodines, Tritium, and Particulates Organ dose rates due to radiciodines, tritiun, and all radioactive materials in particulate fctm with half-lives greater than eight days, will be calculat-ed for the purpose of implementation of Technical Specification 3.11.2.1.b as follows: D, = organ dose rate at time of release (mrem /yr) i X/Q (P Q{} i = yg I 0D04, Fermi-2 2.0-7 4 2673W/0051W, 05/24/84 j 3. __..s-_.--._..-._.._j

wher]. X/Q = the highest annual average relative concentration in any sector at the site boundary. (The highest annual average or the annual average determined for the particular release point may be used.) = 4 186 x 10-6 sec/m in the NW sector (highest annual average) l 3 P = organ dose parameter for organ o and radionuclide i, (mrem /yr per gg 3 pCi/m ) for inhalation determined as follows: P = K (BR) DF yg h and where 6 constant of unit conversion,10 Ci/pCi K = breathing rate for child age group BR = 3 3700 m / year (Table 2.2-10) (from Reference 3) = gg = inhalation pathway dose factor for child age grot:p for DF organ o and radionuclide 1 (Table 2.2-2) (from Referenc:t 3) 1 Qj, = release rate of non-noble gas radionuclide 1 (required by Technical j j Spe::ification 3.ll.2.1.b)(pCi/sec) for the type of release under j consideration. NOTE: In order to assure that potential dose rates (pre-release) to an organ due to radiciodine, tritium and particulates in simultane-ous gaseous releases from the site do not exceed 1500 mrem / year as specified in Technical Specification 3.ll.2.l(b), potential organ dose rate D must be limited as follows: g Do+ (B x SF) < 1500 mrem / year 0004, Fermi-2 2.0-8 2673W/0051W, 05/24/84

.\\ where B cnd SF are es:1gned the same values es w:re used in Section 2.1 for the release source pathway under consideration. To further ensure that dose rate limits were not exceeded, (post-release) dose rates from simultaneous releases shall be summed. 2.2.2 UNRESTRICTED AREA AIR DOSE AND DOSE TO INDIVIDUAL 2.2.2.a Ain. Dose in Unrestricted Area For the purpose of implementation of Technical Specifications 3.11.2.2 and 3.11.2.4, the air dose in unrestricted areas shall be determined as follows: D = air dose due to gamma emissions from noble gas radionuclide 1 (mrad) Y [ ~M1, y (X/O ( ~~ ~8 3.17 x 10 = where -8 3.17 x 10 = the fraction of one year per one second = cumulative releace of noble gas radionuclide i over the period of interest (pCi) for the type of release under consideration. M = defined in Section 2.1.1 y X/Q = 4.186 x 10-6 sec/m3 in the NW sector (This is the highest annual average; the annual average for the particular release point may be used iY desired). D = air dose due to beta emissions from noble gas radionuclide 1 (mrad). g ,y (X/Q) ( = 3.17 x 10-8 N N = air dose factor due to beta emissions from noble gas radionuclide 1 y 3 (mrad /yr per pCi/m from Table 2.1-1). ODN, Fezmi-2 2.0-9 2673W/0051W, 05/24/84 i-

2.2.2.b Dos 7 To An Individual In Unrestricted Arel Dose to an individual from radioiodines, tritium, and radioactive materials in particulate form will be calculated for the purpose of implementation of Technical Specifications 3.11.2.3 and 3.11.2.4 as follows: = dose to an organ of an individual from radiciodines, tritium, and Dj-radionuclides in particulate form (mrem). I 3.17 x 10 W' (R,fp) QQ -8 = where -8 3.17 x 10 = fraction of one year per one second. W' = pathway-dependent relative dispersion for p unrestricted areas at the controlling sector. r /Q' = annual average relative dispersion parameter for T location of controlling critical receptor. X7Q' applies to inhalation and all tritium pathways only. (For all tritium pathways, the b,' scurce term is limited to tritium.) = 2.636 x 10'7 sec/m' in the WNW section for inhalation and all tritium pathw&ys. W'= p D/Q' = annual average deposition parameter for location of controlling (critical) receptor. D/Q' applies to all other pathways. = 2.763 x 10' ' m in WNW sector for all other -2 C pathways. 00CM, Fermi-2 2.0-10 2673W/0051W, 05/24/84

=.. (NOTE: One or both dispersion values (X/Q' and/or D/Q') may be required in the determination of organ doses to an individual depending upon the organ dose pathway present and applicable to the critical receptor.) k'- = cumulative release of radionuclide 1 (required by Technical Specifi-cation 3.11.2.3) over the period of interest (pCi). (For tritium pathways, the %' source term is limited to tritium.) R = pathway-specific, individual age-specific, organ dose factor for radionuclide i, pathway p, organ j, and individual age group, a. The controlling individual age group and the dose pathways are is determined through the Land Use Census for the site. R,yp) determined as follows: (NOTE: At Fermi-2 Plant the controlling receptor is an infant. The dose pathways are inhalation, ground-plane, and grass-goat-milk). Inhalation Pathway Factor R,gg) K'(BR), (DFA ), mrem /yr per pCi/m 3 u where 6 K' = constant of unit conversion 10 pCi/ C1 (BR), = the breathing rate for a particular age group in m / year from Table 2.2-10. (infant = 1400) (OFA = the inhalation dose factor for receptor age group a and for radionuclide 1, in mrem /pCi from Tables 2.2.-l through 2.2-4. (Infant, Table 2.2-1) ODO4, Fermi-2 2.0-11 2673W/00SlW, 05/24/34

q I Ground-Plane Pathwxy Facttr 2 mrem / year per pCi/sec) Ralpj K'K" (SP) (DFG j) ((1-e )/A1) (m i = K' = constant of unit conversion,10 pCi/pC1. K" - = constant of unit conversion, 8760 hr/yr. 1. SF' = shielding factor, 0.7 (dimensionless) DF( = ground plane dose conversion factor for radionuclide 1 (same for 2 all age groups) (mrem /hr per pC1/m ) Table 2.2-9. 1 = decay constant for radionuclide 1. 1 8 t = exposure time, 4.73 x 10 sec (15 years). Grass-Goat-Milk Pathway Factor -A t f f, + (1-f f,)e ih ,-A tg7 g(U,p) p p m(#}(bj,a b Y Y alpj Ay+A, p 3 (m mrem /yr per pCi/sec) where (NOTE: Fermi-2 Plant Site-Specific values are included in parentheses fallow-ing each definition.) 6 K' = a constant of unit conversion,10 Ci/pCi. s = the goat's consumption rate, in kg/ day (wet weight). (6) U,p = the receptor's milk consumption rate for age group a, in liters /yr from Table 2.2-10. (infant - 330) ODCN, Fermi-2 2.0-12 2673W/0051W, 05/24/84

Y = the cgricultural productivity by unit area of pastura feed grass, in p 2 kg/m, (0.7) 2 Y, = the agricultural productivity by unit area of stored feed, in kg/m, (2.0) F, = The stable element transfer coefficients, in days / liter. (see Table 2.2-11.) r- = fraction of deposited activity retained on feed grass. l (1.0 for radiciodines; 0.2 for particulates) (DF )a = the organ ingestion dose factor for the ith radionuclide for the receptor in age group a, in mrem /pCi from Tables 2.2-5 through 2.2-8. (infant - Table 2.2-5) ~ 1 = the decay constant for the ith radionuclide, in sec A A, = the decay constant for removal of activity on leaf and plant sur-4 faces by weathering, 5.73 x 10-7 ~1 sec (corresponding to a 14 f day half-life). t = the transport time from pasture to coat, to milk, to receptor, in y sec. 7 j (1.73 x 10, t = the transport time from pasture, to harvest, to goat, to milk, to h 6 receptor, in sec. (7.78 x 10 ) f = fraction of the year that the goat is on pasture (dimensionless). p (.5) f, = fraction of the goat feed that is pasture grass while the goat is on pasture (dimensionless). (.5) 0D04, Fermi-2 2.0-13 2673W/0051W, 05/24/84

Fcr tritium in tilk, the grass-goat-milk pathway fcctor is a special c sa due to the fact that the concentration of tritium in milk is bas:d on airborna concentration rather than deposition: 3 R,gp) = K'K"' F,Qg,p(DFL )), [0.75(0.5/H)] (mrem /yr per pCi/m ) g ) where: 3 Km- = h* constant of unit conversion,10 gm/kg. H = absolute humidity of the atmosphere, in gm/m. (8) O.75 = the fraction of total feed that is water. 0.5 = the ratio of the specific activity of the feed grass water to the atmospheric water. and other parameters and values are given above. 2.2.2.c Dose Calculations To Support Other Specific Technical Specifications 4 For the purpose of implementing STS 6.P.l.9 dose calculations will be per-I formed using tne above equations with the substitution of average meteorologi-cal parameters for the period of the report, and the appropriate pathway are determined in receptor dose factors (R, ). (Values for R,gp) accorcance with Section 2.2.2,d.) For the purpose of implementing STS 6.9.1.11, dose calculations may be per-formed using the above equations with the substitution of the dispersion para-meters (X/Q, D/Q) which are concurrent with actual releases, and the appropri-ate pathway receptor dose factors (R,y ) (Values for R,gpj are deter-mined in accordance with Section 2.2.2.d) pj. ODCM, Fermi-2 2.0-14 2673W/0051W, 05/24/84

For the purpose of implclenting STS 3.12.2, dose calculations may be per-formed using the cbova equations substituting tha cppropriate pathray receptor dose factors (Rhipj) and the appropriate dispersion parameters for the loca-tion (s) of interest. Annual average dispersion parameters (6 month average for D/Q) may be used for these calculations. (Values for Raipj are deter-mined in accordance with Section 2.2.2.d). 2.2'.2.d Additional Pathway Dose Factors ~ For the purpose of implementing STS 6.9.1.9, 6.9.1.11 or 3.12.2, it may be necessary to calculate individual doses due to gaseous releases via exposure f pathways other than ground plane, inhalation, and grass-goat-<nilk pathways presented in Section 2.2.2.b. Methodology for calculating doses due to gaseous releases via the grass-cow-milk, grass-cow-meat and the vegetation pathwa[is the same as was presented in Section 2.2.2.b. However, R,fp) is pathway-dependent and is calculated for the remaining pathways as follows: Grass-Cow-Nilk Pathway Factor ~ t R,fp) K, Ag (U,g) F, M % p,p s + Il~I I ), ff yh ,-A tfg ps = y y

i. w 2

s (m mrem /yr per pCi/sec) where (HnTE: Parameter values given in parentheses are to be used in lieu of site-specific values. (Reference 3.)) 6 K' = a constant of unit conversion,10 Ci/pC1. l g = the cow's consumption rate, in kg/ day (wet weight). (50) U,p = the receptor's milk consumption rate for age group a, in liters /yr from Table 2.2-10. ' NOTE: These pathways do not presently exist. Methodology is presented for use in the event that subsequent land use census results indicate i such a requirement. l 0004, Fermi-2 2.0-15 2673W/0031W, 05/24/84

Y = the cgricultural productivity by unit arco of pasture feed grass, in p 2 kg/m, I (0.7) 2 Y, = the agricultural productivity by unit area of stored feed, in kg/m, (2.0) F, = The, stable element transfer coefficients, in days / liter. (see Table 2.2-11.) r = fraction of deposited activity retained on feed grass. (1.0 for radiolodines; 0.2 for particulates) (DF ), = the organ ingestion dose factor for the ith radionuclide for the receptor in age group a, in mrem /pCi from Tables 2.2-5 through 2.2-8. ~1 A = the decay constant for the ith radionuclide, in sec g A, = the decay constant for removal of activity on leaf and plant ~7 ~ surfaces by weathering, 5.73 x 10 sec (corresponding to a 14 day half-life). t = the transport time from pasture to cow, to milk, to receptor, in g sec. 0 (1.73 x 10 ) t = the transport time from pasture, to harvest, to cow, to milk, to h 6 receptor, in sec. (7.78 x 10 ) f = fraction of the year that the cow is on pasture (dimensionless). p (0.5) f = fraction of the cow feed that is pasture grass while the cow is on s pasture (dimensionless). (0.5) 00CM, Fermi-2 2.0-16 2673W/0051W, 05/24/84

l Fcr' tritium in cilk, the grass-cow-<nilk pathw y ftctor is a special crse due to the fact that the concentration cf tritium in milk is based on airborns concentration rather than deposition: R,gp) =K'K'"F,Qg,p(DFLg), [0.75(0.5/H)] (mrem /yr per pCi/m ) where: K'", = a, constant of unit conversion,10 gm/kg. H = absolute humidity of the atmosphere, in gm/m. (8) 0.75 = the fraction of total feed that is water. 0.5 n the ratio of the specific activity of the feed grass water to the atmospheric water. and other parameters and values are given above. Grass-Cow-Neat Pathway Factor 4t l 4(U,p)F(r)(DFL f f, (1-f f )e 1h ,-l tf7 p p3 7 fj ), R,fp) K, y + = y y 2 i. (m mrem /yr per yCi/sec) i 1 l where I (NOTE: Parameter values given in parentheses are to be used in lieu of site-specific values. (Reference 3)) 6 K' = a constant of unit conversion,10 C1/pCi. i = the cow's consumption rate, in kg/ day (wet weight). (50) 0D04, Fermi-2 2.0-17 2673W/0051W, 05/24/84 =, -,. _. - - - -. - - -. - - -.. -.,. y, - - - - ,-.-.----.,,-.-,m. ---.-e-p.y-,- r-.

--- ~' U,p = the receptor's meat consumption rita for age group a, in kg/yr from Table 2.2-10. Y = the agricultural productivity by unit area of pasture feed grass, in 2 kg/m, (0.7) Y, = the agricultural productivity by unit area of stored feed, in kg/m. (2.0) F = The stable element transfer coefficients, in days /kg. 7 (see Table 2.2-11.) r = fraction of deposited activity retained on feed grass. (1.0 for radiciodines; 0.2 for particulates) (DFhy), = the organ ingestion dose factor for the ith radionuclide for the receptor in age group a, in mrem /pCi from Tables 2.2-5 through 2.2-8. A = the decay constar.t for the ith radionuclide, in sec 1 A, = the decay constant for removal of activity on leaf and plant sur- -1 (corresponding to a 14 10,~7 sec j faces by weathering, 5.73 x day half-life). t = the transport time from pasture to cow, to meat, to receptor, in g sec. 6 (1.73 x 10 ) t = the transport time from pasture, to harvest, to cow, to meat, to h 6 receptor, in sec. (7.78 x 10 ) f = fraction of the year that the cow is on pasture (dimensionless). p (0.5) 0D04, Fermi-2 2.0-18 2673W/0051W, 05/24/84

f, = fraction of the cow feed that is pasture grass while the cow is on pasture (dimensionless). (0.5) For tritium in meat, the grass-cow-meat pathway factor is a special case due to the fact that the concentration of tritium in meat is based on airborne concentration rather than deposition: 3 = K'K'"F Q U,p(DFL ),- [0.75(0.5/H)] (mrem /yr per pC1/m ) R,gp) 7p where: 3 Ki" = a constant of unit conversion,10 gm/kg. H = absolute humidity of the atmosphere, in gm/m. (8) 0.75 = the fraction of total feed that is water. 0.5 = the ratic of the specific activity of the feed grass water to the atmospheric water. and other parameters and values are given above. Vegetation Palhway Factor

  1. t,{

U fe it+d I i r = K' (DFLg), R,1 ) gg as g' where (NOTE: Parameter values given in parentheses are to be used in lieu of site-specific values. (Reference 3)) 6 K' = a constant of unit conversion,10 pCi/pCi. 00CN, Fermi-2 2.0-19 2673W/0051W, 05/24/84

TABLE 2.2-10 I!OIVIOUAL USAGE FACTORS

  • IWANT CHILD _

TEENAGER _ ADULT p Milk Consumption Rate, 330 330 400 310 Sp-(liters / year) Meat Consum'tfon Rate, p 0 41 65 110 i U,p (kg/ year) Fresh Leafy Vegetation Constsnption Rate, Ug -(kg/ year) 0, 26 42 64 Stored Vegetation Consumption Rate, 0 520 630 520 Ss(kg/ year) Brgathing Rate (m'/ year) 1400 3700 8000 8000 t f

  • Reference 3, Table E-5.

i 2.0-51 0D04, Fermi-2 2673W/0051W, 05/24/84

TABLE 2.2-11 STABLE ELEMENT TRANSFER OATA* m -(COW) m(- MILK Fr - MEAT MILK F ELEMENT F GOAT) H 1.0E-02 1.7E-01 1.2E-02 1.2E-02 1.0E-01 3.1E-02 C 4.0E-02 4.0E-02 3.0E-02 l3 Na ~* l l P 2.5E-02 2.5E-01 4.6E-02 Cr 2.2E-03 2.2E-03 2.4E-03 Mn 2.5E-04 2.5E-04 8.0E-04 Fe 1.2E-03 1.3E-04 4.0E-02 Co 1.0E-03 1.0E-03 1.3E-02 Ni 6.7E-03 6.7E-03 5.3E-02 Cu 1.4E-02 1.3E-02 8.0E-03 Zn 3.9E-02 3.9E-02 3.0E-02 Rb 3.0E-02 3.0E-02 3.1E-02 Sr 8.0E-04 1.4E-02 6.0E-04 Y 1.0E-05 1.0E-05 4.6E-03 Zr 5.0E-06 5.0E-06 3.4E-02 Nb 2.5E-03 2.5E-03 2.8E-01 Mo 7.5E-03 7.5E-03 8.0E-03 Tc 2.5E-02 2.5E-02 4.0E-01 l Ru 1.0E-06 1.0E-06 4.0E-01 i Rh 1.0E-02 1.0E-02 1.5E-03 Ag 5.0E-02 5.0E-02 1.7E-02 Te 1.0E-03 1.0E-03 7.7E-02 I I 6.0E-03 6.0E-02 2.9E-03 Cs 1.2E-02 3.0E-02 4.0E-03 Ba 4.0E-04 4.0E-04 3.2E-03 La 5.0E-06 5.0E-06 2.0E-04 Ce 1.0E-04 1.0E-04 1.2E-03 Fr 5.0E-06 5.0C-06 4.7E-03 Nd 5.0E-06 5.0E-06 3.3E-03 W 5.0E-04 5.0E-34 1.3E-03 Np 5.0E-06 5.0E-06 2.0E-04 i

  • References 3, Table E-1.

000M, Fermi-2 2.0-52 2673W/0051W, 05/24/84

2.3 ' METEOR 0 LOGICAL MODEL 2.3.1 ATMOSPHERIC DISPERSION Atmospheric dispersion for releases is calculated using a mixed-mode form of the straight line flow Gaussian model. X/Q = average atmospheric dispersion (sec/m ) for a given wind 'd'ifection (sector) and distance. l 1 E . (1-E) exp (-1/2 (h/oj) ) = 2.03 6 K j Nr ujk*j UjkDj l 2.03 = (2h )l/2 divided by the width in radians of a 22.50 sector (0.3927 radians). = number of hours meteorological conditions are observed to be in a njk given wind direction, windspeed class k, and atmospheric stability classJ. NOTE: If periodic data (hourly) are used instead of the joint fregaency data, all variable subscripts are dropped, the n is set equal jy to 1 and the hourly averaged meteorological variables are entered into the model. i = total hours of valid ceteorological data throughout the period of N effluent release. = distance from the release point to location of interest (meters) r = wind speed (midpoint of windspeed class k) measured at the 10 meter ujk level (m/sec) during atmospheric stability class j U = wind speed extrapolated to the effective release height using the p wind power law with the site-specific wind power law exponent. ODCM, Fermi-2 2.0-53 2673W/0051W, 05/24/84

(a)2 + b /2n)12 2 Ij = the lesser of or where (/3 oj) = vertical standard deviation of the plume (meters) at distance r for f oy releases under the stability category j indicated by AT, from Figure 2.3-1. I K = terrain recirculation factor from Table 2.3-1. = plume depletion factor (radiciodines and particulates) at distance ~6 r for the applicable stability class. Normally a factor of 1 is assumed or, if appropriate, may be obtained from one of Figures 2.3-2 through 2.3-5. = 3.1416 n = maximum height of adjacent building either upwind or downwind from b the release point. L AT = vertical temperature gradient (oC/100m). E = fraction considered as ground level releases l 1 W ~ i 1.0 for R$ 1.0 u i i 2.58 - 1.58 ( o ) for 1.0 < 1 1.5 u u E = - 0.06 ( Oi for 1.5 < b 5.0 i 0.3 u u i W l 0 for _.9 > 5. 0 u 4 i 4 2.0-54 0004, Fermi-2 2673W/0051W, 05/24/84

W = v;rtical cxit valocity from the vent. g = horizontal wind speed' at the point of release. u h = effective height of release (m) h = 4 + hr - c y h = height of release point y hr = additional height due to plume rise (m): for neutral or unstable conditions (aT < -0.5 oC/100n) ) 2/3 1/3 I 1.44 ( Di (I) d I u d h = the lesser of or pr W 3 ld j u for stable conditions (AT > -0.5 oC/100m): 1/4 4 (F'm) S l I l or II3 I 1.5 (F' 1 3 -1/6 m hr = the lesser of p u or tbr for neutral or unstable conditions (in the event that tbr for neutral or unstable conditions. is less than h for stable pr _ conditions) d = diameter of plant vent c = correction for low vent exit velocity (m) v 00CM, Fermi-2 2.0-55 2673W/0051W, 05/24/84

r =- 3(1.5 b d for b< 1.5 u u _ C = y 0 for > 1.5 u 4 2 momentum flux parameter (m /sec ) F, = F,'. . (W )2 (d/2)2 g S = restoring acceleration per unit displacement ~4 ~ 8.75 x 10 sec for -0. 5 < A T < 1. 5 ~3 -2 1.75 x 10 sec for

1. 5 < A T < 4. 0 S

= -2 ~ 2.45 x 10 sec for A T > 4. 0 2.3.2 RELATIVE DEPOSITION Relative deposition per unit area is calculated for a mixedwnode releasa. (m-2), for a given wind D/Q = relative deposition per unit area direction and at a given oistance. = 2.55K [(E) (g ) + (1 - E) D ], where r e D = relative deposition mode for the ground-level portion of mixed-mode g releases from Figure 2.3-6. D = relative deposition rate for the elevated portion of mixed-mode l l releases obtained from one of Figures 2.3-7 through 2.3-9. 4 2.55 = [ radians per 22.50 Sector]~1 l ODCN, Fermi-2 2.0-56 2673W/0051W, 05/24/84

1 s y8 SITE (OISTANCE-0.8km 1.2 km L. ;km 2.4km 3.2km 4.0km 4.8km 5.6km 6.4km 7.2km 8.0km BOUNDARY METERS) 0.5mi 0.75mi T.tani 1.5ml 2 mi 2.5ml 3.0m1 3.5mi 4.0mi 4.5mi 5.0mi {9 N 1.13 (1249) 1.11 k.13 1.14 1.15 1.16 1.18 1;20 1.14 1.08 1.06 1.04 $ e7 P NME 1.32 (1646) ,1.23 1.27 1.32 .. 1.35 k.34 1.40 1.39 1.35 1.32 1.29 1.26 Yf 4 k SSE 1.58 (610) 1.61 i.67 1.73 1.79 1.76 1.69 1.66 1.51 1.44 1.46 1.37 5 1.57 (1417) 1.39 1.51 1.62 1.67 $.60 1,69 1.65 1.60 1.51 1.39 1.32 .1.24 1.15 1.07 1.01 SSW 1.14 (1542) 1.07 1.11 1.14 1.21 1.25 1.24 1.28 SW 1.43 ,(1920) 1.31 1.35 1.40 1.48 1.56' ' 1.61 1.10 1.59 f.57 1.53-1.46 WSW 1.25 (1798) 1.17 1.21 1.24 1.29 1.32 1.38 1.38 1.31 1.23 1.18 1.18 k.31 1.23 1.27 m W 1.20 (13iO) 1.12 1.18 1.23 1.30 1.34 -1.32 1.38 1.38 WNW 1.08 (1082) 1.05 1.09 1.12 1.16 1.16 1.20 1.26 1.30 i~.26 1.14 1.08 p MW 1.18 (915) 1.16 1.22 1.27 1.29 1.26 1.40 1.44 1.41 1.34 1.27 1.26 NNW 1.35 (990) 1.34 1.36 1.37 1.40 1.43 1.49 1.64 1.57 1.44 1.34 1.27 1.inear interpolation within a sector at distances lying between those shwon in the. table is [F-F 4(12-FR IN 21 given by: 2 1 R

  • (N-Rj 2

1) ~ 2 g Where R, is that distance lying between the distances (Rg & R ) specified in the table. 2 F &F are the values at these specified distances. 3 2 t 1 1 l TABLE 2.3-1 Open Terr.In Recirculation Factor i c

FIGURE 2.3-1 Vertical Standard Deviation of Material in a Plum] (o )# 7 (Letters denote Pasquill Stability Class) j 1 i 1000 l l ,/ / / ~ /~ / / / l / / s / / l } r f / / / / / / / / [ A 100 / / i / / i,B / / / / / i / / / / / s / / / / / / .c / / / / / f/ f ~ 0 / / / f ~ ~~~~ O f,/ y y /// / e / / / /,,/ / G 10 l / / / / / / _/ / / / ,/ / ~~ / f, / 0.1 1.0 10 100 F'LUME TRAVEL DISTANCE (KILOMETERS) Temoerature Channe Pasquill Stability withHeicht(k)(UK/100m) Catenories Classification j <-1.9 A Extremely unstable -1 9 to -1.7 8 Moderately unstable -1.7 to -1.5 C Slightly unstable -1.5 to -0.5 0 Neutral

  • Reference 6

-0.5 to 1.5 E Slightly stable 1.5 to 4.0 F Moderately stable > 4.0 G Extremely stable ODCN, Femi-2 2.0-58 2673W/0051W, 05/24/84

FIGtRE 2.3-2 e Plune Depletion Effect~for Ground-level Releases (All Atmospheric Stability Classes) o Nn j O. 1 8 s / / I g / 3 i / u kE r 1G Es E5 El j oas ee< I EN I mg / u / II / ge oi / id *.i / Ri e =E >-we 23 3: E o"5 a I 8 i

  • 2

/ a I I 3E -6 e o e m e M N n Q d 6 6 6 o d O O O e fere e 6 3MfMd NI DNINIYW3M NOllDVWd 2.0-59 0D04, Fermi-2 2673W/0051W, 05/74/84

FIGURE 2.3-3 Pltna Depiction Effcct for 30-m Releasts (Letters denote Pasquill Stability Class) o-( f f R O. i r 1 8 I / / e lb -~~' / / /// / // 1 <o e d ~m' } (u. h w z "- g r 4 DS g a W B t E I 0 i 11 y I IJ g 1 II ~ 11 8 d g // i j H mi a a = [/ a s z 5 E a J w E !E i i 8 o a e e f l II II i II l ll ? 'l I l 1 r i I 1 l n* i I o M M N o 9

  • .M N

5 ~ o e o o o e o o o % fere me 6 3Wnld NI DNINIYW5W NOll3WWd j ODCN, Fermi-2 2.0 2673W/0051W, 05/24/84

]1 ! ml"NY> 35hEg8 4?"" on s4 &E 0 k h ag E 2*E0" wi0?x C E 0 0 5 \\ ( Qg I S z NEUTRAL (D) Q gp 10-5 STABLE E j m 1 ,~ + a m s / / A'N\\ w / f N s a / / N j x 3 = STABLE (E,F,G) I I f I r / I { 10-7 I J 0.1 1.0 10.0 100.0 200.0 PLUME TRAVEL DISTANCE (KILOMETERS) Relative Deposition for 30m Releases (Letters denote Pasquilt Stability Class)

  • Reference 6
2. 0-M 0D04, Fermi-2 2673W/0051W, 05/24/84

,n ww r---,n,---,+----,-r----,,c.


,-,,-,,,-,,n-

,-,,--.w~. ,,--,r--r-s-----,--m,mewes,.,m--,-,-,-,-,---wr,-e, e.,,v-e-,-w-r

FIGURE 2.3-8 Relative Deposition for 60-m Releases (Letters dencte. Pasquill Stability Class) 104 I UNSTABLE (A,B,C) [ \\ / K r s ig 6 f NEUTRAL (D) ( / / Q r i A w I I W f / N% E / \\ 5 UNSTABLE / \\ E NEUTRAL a r s 3 s, i 1-N I e i E I / s i 3:: 5 l IE } ggy7 J STABLE (E,F.G) r I J i J J l I I I l I i I I i r 104 I J 0.1 1.0 10.0-100.0- 200.0 { PLUME TRAVEL DISTANCE (KILOMETERS) Relative Deposition for 60<n Releases (Letters denote Pasquill Stability Class) e Reference 6 ODO4, Fermi-2 2.0-65 2673W/0051W, 05/24/84 m w -- ~,-,~w


.--,m,

.---n.--w-- ,-----,.,.n,


,w.

-,-v m-

FIGtRE 2.3-9 Relative Deposition for 100-m Releases (Letters denote Pasquill Stability Class) 104 "t i _UNSTABL E ( A.8,C) 3 ~%\\ s 10-5 p L l l ~ r s w f f NEUTRAL (0) k g E / / A N l c E / / N N E f N h 104 t l l E i i E I i y / / r p r 5 A E STABLE (E,F,G) NO DEPLETION l I / f 104 0.1 '1.0 10.0 100.0 200.0 PLUME TRAVEL DISTANCE (KILOMETERS) Relative Deposition for 100e Releases (Letters denote Pasquilt Stability Class)

  • Reference 6 0004, Fermi-2 2.0-66 2673W/0051W, 05/24/84

2.4 DEFINITIONS OF GASEOUS EFFLUENTS PARAMETERS Section of Term Definition Initial Use B = administrative allocation factor for gaseous 2.1.1 effluent pathways. b = maximum height of the adjacent building. 2.3.1 monitor reading of a gaseous effluent monitor corre-2.1.1 C = sponding to associated sample radionuclide concentrations. D organ dose rate at time of release (mrem /yr) 2.2.1.b = D dose to an individual from radiciodines, tritium, and radio-2.2.2.b = p nuclides in particulate form with half-lives greater than eight days (mrem). skin dose rate atitime of release (mrem /yr) 2.2.1.a D = s D total body dose rate at time of release (mrem /yr) 2.2.1.a = t D air dose due to beta emissions from noble gases (mrad) 2.2.2.a = O D air dose due to gama emissions from noble gases (mrad) 2.2.2.a = Y D/Q the sector averaged relative deposition for any distance 2.3.2 = in a given sector. D/Q' annual average relative deposition at the location 2.2.2.b = of the maximum exposed individual. 2.763 x 10-9 m-2 n the WNW sector i = 0D04, Fermi-2 2.0-67 2673W/0051W, 05/24/84

Section of Initial U o Term Definition plume depletion factor at distance r for the appro-2.3.1 6 = priate stability class (radiciodines and particulates). total body dose factor due to gamma emissions from 2.1.1 'K = g; radionuclide (mrem / year per pCi/m ) from Table 2.1-1. Skin dose factor due to beta emissions from radionuclide 2.1.1 L = y 3 i (mrem /yr per pCi/m ) from Table 2.1, air dose factor due to gamma emissions from radionuclide 2.1.1 M = g 3 i (mrad /yr per pCi/m ) from Table 2.1-1. air dose factor due to beta emissions from noble gas 2.2.2.a N = g 3 radionuclide 1 (mrad /yr per pC1/m ) from Table 2.1-1. i number of hours meteorological conditions are 2.3.1 n = jk observed to be in a given wind direction, wind-J speed class k, and atmospheric stability class J. total hours of valid meteorological data. 2.3.1 N = dose parameter for radionuclide i, (mrem /yr per 2.2.1.b P = y { pCi/m ) for the inhalation pathway from Table 2.2-1. rate of release of noble gas radionuclide i 2.1.1 j Q = g (p Ci/sec) release rate of radionuclide i for the combined source 2.1.2 Q' = g terms of routine Reactor Building Exhaust Plenum plus Containment Drywell Purge Release. cumulative release of noble gas radionuclide i over 2.2.2.a k = the period of interest (pC1). OD(N, Fermi-2 2.0-68 2673W/0051W, 05/24/84

Section of Term Definition Initial Usn cumulative release of radiciodine, tritium or 2.2.2.b = material in particulate form over the period of interest (pCi). .r, ate of release of noble gas radionuclide 1 (pCi/sec) 2.1.3 q1 = from the Containment Drywell Purge. dose factor for radionuclide i, (mrem /yr per pCi/m ) 2.2.2.b R = y 2 or (m -mrem /yr per pCi/sec). monitor reading per mrem /yr to the skin. 2.1.1 R = 3 m nitor reading per mrem /yr to the total body. 2.1.1 R = t limiting dose rate to the total body 2.1.1 D = TB 500 n. rem / year. = limiting dose rate to the skin 2.1.1 D,, = 3000 mrem / year. = =, distance from the point of release to the location 2.3.1 r of interest for dispersion calculations (meters). monitor reading of the noble gas monitor at the alarm 2.1.1 C = 3 setpoint for the release pathway under consideration. vertical standard deviation of the plume with 2.3.1 I) = building wake correction. vertical standard deviation of the plume (in meters), 2.3.1 oy = at distance r for ground level releases under the stability category j indicated by AT, from Figure 2.3-1. vertical temperature gradient (oC/100m). 2.3.1 l AT = 00CM, Fermi-2 2.0-69 2673W/0051W, 05/24/84

S;ction of Initial Use Term Definition 2.3.1 terrain recirculation factor. K =- wind speed (midpoint of windspeed class k) at ground 2.3.1 u = jk level (m/sec) during atmospheric stability class j. e s relative dispersion for unrestricted areas at the 2.2.2.b W', = controlling receptor. the sector-averaged relative concentration at any distance 2.3.1 X/Q = 3 r in a given sector. (sec/m ) the highest annual average relative concentration in 2.1.1 Y75 = any sector, at the site boundary. sec/m 3 4.186 x 10 sec/m in the NW sector = relative concentration for the location occupied by 2.2.2.b 'X7Q' = the controlling receptor. -7 3 2.686 x 10 sec/m in the NNW sector = windspeed u extrapolated to the effective release 2.3.1 U = jk height using the wind-height power law. fraction of release considered as ground-level 2.3.1 E = 4 -2) 2.3.1 momentum flux parametar (m sec F,' = effective release height (m) 2.3.1 f h = 1 height of release point (m) 2.3.1 h = y ODCM, Femi-2 2.0-70 2673W/0051W, 05/24/84

Section of Initial Use Term Definition 2.3.1 . g, _ = additional height due to plume rise (m) stack Exit velocity (m sec-1) 2.3.1 W, = i 2.3.1 r,e, storing acceleration per unit displacement for S = adiabatic motion in the atmosphere. (sec~ ) horizontal wind speed at the point of release 2.3.1 u = 3 54 + 00CM, Fermi-2 2.0-71 2673W/0051W, 05/24/84

2.5 GASEOUS RA0 WASTE EFFLUENT SYSTEM AND VENTILATION EXHAUST TREATMENT SYSTEM Figure 2.5-1 is a schematic of the Gaseous Radwaste Effluent System showing the release points to unrestricted areas. The Ventilation Exhaust Treatment System is also presented in Figure 2.5-1. The Ventilation Exhaust Treatment System consists of EPA filters installed in the Service Building Ventilation -System and -HEPA and charcoal filters installed in Radwaste Building VenlilationSystem. 0D04, Fermi-2 2.0-72 2673W/0051W, 05/24/84

._m. - - - - - - - - ------- --,---w .--w .-__..=.--.---w-4.- .-+4 _m --=4, + --N = * - 9 M ,q i.izh. ~ N 9tt-ses g L s. ea b oR .= f17 y ag' ,t~I_ {g{ F s' = is = / -i-, 7 g ff(. g e *" ~ = n i e g "" 'h W j = - li; (({ y ,._, r (f(. t

  • e

-e.: = -___._,s _m._ 3 si n sis-.eos i g ,M E M ~ 33 i e r i i c [ w l =n=, O I : is 1 o

== a a A E r i f-, i llllt V 8 !!!-llll: y a m "=" L i { <M' 3 W F V m. l GASEOUS RADWASTE EFFLUENT SYSTEM = =,= = =m. M i

SECTION 3. RADIOLOGICAL ENVIRONKNTAL MONITORING PROGRAM 3.1 SAWLING LOCATIONS Sagling locations as required in Technical Specification 3/4.12.1 are described in Table 3.0-1 and shown on the maps in Figures 3.0-1, 3.0-2, and 3.0-3. t NOTE: For the purpose of implenenting Technical Specification 3.12.2, sagling locations will be modified as required to reflect the findings of the Land Use Census. t I I l i ODCM, Fermi-2 3.0-1 2767W/0051W, 05/24/84

TABLE 3.0-1 ENVIRONM.NTAL RADIOLOGICAL MONITORING PROGRAM (Sampling Locations) Station Distance fran Nunber Direcian Reactor (Approx) Description Media Frequency 1 NE 1.3 mi. Estral Beach (conmmity) Direct Radiation Q Pole on Lakeshore,18 Radiciodine W Poles S. of Lakeview Particulates W ~~ 2 ME 1.1 mi. Tree at the terminatim Direct Radiation Q Brancho Street (private residence) 3 N 1.1 mi. Pole at NW corner of Direct Radiation Q Swan Boat Clth Fence (Ccmnmity) 4 NNW 0.6 mi. Site Bomdary and Toll Direct Radiation Q Road, on Site Fence by Radiciodine W APS #4 5 NW 0.6 mi. Site Bomdary and Toll Direct Radiation Q Road on Site Fence by Radiciodine W APS #5 Particulates W 6 WNW 0.6 mi. Pole NE corner of bridge Direct Radiation Q over Toll Road 7 W 15 mi. Pole, behind Doty Farm, Direct Radiation Q 7512 N. Custer Road Radiciodine W (control) Particulates W Milk M S-1 NW 2.4 mi. Pole NE corner Dixie Direct Radiation Q Highway and Post Road S-2 M4W 2.4 mi. Pole NW corner Tranbley Direct Radiation Q Road and Swan View Road S-3 N 2.6 mi. Pole on S side Massarant Direct Radiation Q - 2 Poles W of Cinavarre S-4 NNE 6.5 mi. Pointe Mouillee - W. Direct Radiation Q Jefferson and Canpau Road, Pole on SE corner of Bridge S-5 NE 5.1 mi. Pointe Mouillee Game Area Direct Radiation Q 4 - Field Office, Pole near tree north area of parking lot 3.0-2 ODCM, Fermi-2 2767W/0051W, 05/24/84

y TABLE 3.0-1 ENVIRONENTAL RADIOLOGICAL MONITORING PROGRAM (CONTIMJED) ? Station Distance fran - Media Frequency Nunbar Direcim Reactor (Approx) Description S-6 N 4.5 mi. Labo and Dixie Highway - Direct Radiation Q Pole on Sw corner with light S-7 PMW 5.0 mi. Labo and Brandon - Pole Direct Radiation Q on SE caner near RR S-8 NW 4.0 mi. Pole NW corner Newp at Direct Radiaticri Q and Brandon Roads S-9 WNW 4.9 mi. Pole on SE of War and Direct Radiation Q Post Roads S-10 W 5.5 mi. Pole m NE corner Nadeau Direct Radiation Q and Laprad near mobile hone park S-11 SW 4.5 mi. Pole on NW cornir Mentel Direct Radiation Q and Hurd S-12 SW 4.9 mi. Pole in parking lot W Direct Radiation Q Depattment Natural Re-sources Office Building - Sterling State Park S-13 W 2.8 mi. Pole S side Williams Rd. Direct Radiation Q - 8 Poles W of Dixie Hwy. (Special Area) S-14 WSW 2.8 mi. Pole N side of Pearl at Direct Radiation Q Parkview - Woodland Sch. (ptpulated area) S-15 S 0.9 mi. Pole N side of Point Aux Direct Radiation Z Peaux 2 Poles W of Long (site bomdary) S-16 SSW 1.0 mi. Pole S side of Point Aux Direct Radiatim Q Peaux - 1 Pole W of Huron next to vent pipe (site bomdary) S-17 SW 0.9 mi. Fermi gate along Point Direct Radiation Q Aux, Peaux Road - on fence post W of gate (site bomdary) 3.0-3 ODCM, Fermi-2 2767W/0051W, 05/24/84

TABLE 3.0-1 ENVIRONENTAL RADIOLOGICAL MONITORING PROGRAM (CONTINUED) Station Distance from Media. Frequency Nunber Direcian Reactw (Approx) Description S-18 WSW mi 1.2 mi. Pole on Toll Road - 13 Direct Radiation Q i Poles S of Fermi Drive 5-19 W 1.0 mi. Pole on Toll Rd., 6 Direct Radiation Q i Poles S of Fermi Drive S-20 SSW 6.2 mi. Pole NE corner McMillan Direct Radiation Q and East Front Street (Special Area) S-21 SW 10.1 mi. Pole SE corner of Mortar Direct Radiation Q Creek and Laplaisance S-22 SWS 9.9 mi. Pole E side of S. Dixie Direct Radiation Q 1 Pole S of Albain S-23 WSW 8.0 mi. Pole Cluster (St. Mary's) Direct Radiation Q Park corner of N Custer and Dixie (Monroe St.) (N side, next to river) (Special Area) S-24 WSW 9.2 mi. Pole Milton " Pat" Morison Direct Radiation Q Recreational Reserve - N Custer Road (Control) S-25 WNW 10.1 mi. Pole corner Stony Creek Direct Radiation Q and Finzel Roads S-26 NW 8.7 mi. Pole W side Graf ton Road Direct Radiation Q 1 Pole N of Ash /Graf ton intersection S-27 NNW 9.9 mi. Pole E side of Port Direct Radiation Q Creek,1 Pole S of Will-Carlton Road S-28 N 6.9 mi. Pole on S side of S. Direct Radiation Q Huron River Dr. across from Pace Street (Special Area) j 5-29 N 9.5 mi. Pole NE corner of Direct Radiaticri Q Gibraltar and Cahill Roads i 3.0-4 ODCM, Fermi-2 2767W/0051W, 05/24/84

TABLE 3.0-1 ENVIRONENTAL RADIOLOGICAL MONITORING PROGRAM (CONTIMIED) Station Distence fr a Media Frequency Nunber Direcion Reactor (Approx) Description S-30 PNE 9.9 mi. Pole S corner of Adams Direct Radiation Q and Gibraltar (across from Hunbug Marina) 8 S 0.9 mi. Point Aux Peaux, Sediment SA 100-300 f t. offshore sighting directly to land based water tower 9 E 0.2 mi. Fermi-2 discharge, Sediment SA approx. 200 f t. offshare 10 NE 1.1 mi. Estral Beach, approx. Sediment SA 200 f t. offshare sighting directly to land based windmill 11 NNE 9.5 mi. Control in vicinity of Fish SA Celeron Island 12 SSE 0.4 mi. Fermi Unit I Raw Lake Surface Water M Water Intake Strtcture 13 S 1.2 mi. Monroe Water Station Orinking Water M N side of Pointe Aux Peaux 1/2 block W of Long Rd. 14 NE 13 mi. DECO's Trenton Channel Surf ace Water M Power Plant Intake Structure (Screenhouse #2) 15 NPE 20 mi. Detroit (Allen Park) Drinking Water M Water Station 14700 Moran Rd. 16 E 0.4 mi. Fermi-2 discharge Fish SA (approx. 1200 ft. offshore) 17 SW 1.0 mi. Corner of Erie St. and Radiciodine W Point Aux Peaux Rds. Particulates W 18 WSW 2.0 mi. L. Burns Farm Milk M-SM 4352 Pointe Aux Peaux 20 NW 5.7 mi. Reaune Farm Milk M-SM 2705 East Labo 3.0-5 CDCM, Fermi-2 2767W/0051W, 05/24/84

TABLE 3.0-1 ENVIRONE NTAL RADIOLOGICAL MONITORING PROGRAM (CONTINUED) i Station Distance fran Nunber Direcion Reactor ( Apprcx) Description Media Frequency a 22 W 0.6 mi. Outlet Fermi-2 Storm Sediment SA Drains 3 f 31 NW 4.5 mi. Yoas Farm Milk M-SM 3239 Newport Rd. T 32 NNE 4.0 mi. Roland Farm Milk M-SM 9501 Turnpike Hwy. t W1 S 0.4 mi. Approx. 100 ft. W of Gromdwater On flow Lake Erie, S end of reversal former plant citbhouse site SSW 1.0 mi. A ft. S of Pointe Aux Gromdwater On W2 flow Peaux (PAP) Rd. fence, 427 ft. W of where PAP reversal crosses over Stoney Point's western dike W3 SW 1.0 mi. 143 f t. W of PAP Rd. Gromdwater On flow gate, 62 f t. N of PAP reversal Rd. fence W4 WNW 0.6 mi. 42 ft. N of Langton Rd., Gromdwater On flow 8 ft., E of Toll Rd. reversal fence ODCM, Fermi-2 3.0-6 2767W/0051W, 05/24/84

s TABLE 3.0-1 ENVIRONENTAL RADIOLOGICAL MONITORING PROGRAM (CONTINUED) Station Distance fran Media Frequency Nunber Direcion Reactor (Approx) Description 22 W 0.6 mi. Outlet Fermi-2 Storm Sediment SA Drains Milk M-SM 31 NW 4.5 mi. Yoas Farm 3239 Newport Rd. Milk M-SM 32 NNE 4.0 mi. Roland Farm 9501 Turrpike Hwy. W1 S 0.4 mi. Approx.100 f t. W of Grotndwater On flow Lake Erie, S end of reversal f armer plant citbhouse site W2 SSW l.0 mi. A f t. S of Pointe Aux Gromdwater On flow Peaux (PAP) Rd. fence, reversal 427 ft. W of where PAP crosses over Stoney Point's western dike W3 SW l.0 mi. 143 f t. W of PAP Rd. Grotndwater On flow gate, 62 ft. N of PAP reversal l l Rd. fence W4 WNW 0.6 mi. 42 f t. N of Langton Rd., Grotndwater On flow 8 ft., E of Toll Rd. reversal fence 3.0-6 f 00CM, Fermi-2 2767W/0051W, 05/24/84

~. FIGURE 3.0_1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM - SAMPLING LOCATIONS BY STATION NUMBER (IP9tEDIATE AREA) i t N 4 f \\$ i i l \\ h \\ \\ 4 1 p '%, } k('%,, )' s. s S' AN CREEK -5 go 7,- s-

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~~ [ % ft 2f p 5'[ - g SCAtt or uitE s e -( s-se D 1 p s-i -is a LEGEND i t-g ER E o o A CULATES Y \\ gp g DR ER/ SURFACE WATER I e Q u1LK i [ / [S-34 FIGURE I i I' SAMPLING LOCATIONS Bf STATION NUMBER r (SITE AREAD i L-

.) FIGURE 3.0-2 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM - SAMPLING LOCATIONS BY STATION NUMBER-(GREATER THAN 5 MILES) I 2 j 27% . M.. ) r' "R -- 'g W NDSOR g _M: Last [159 s C inu ,m. i l M%

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ARBOR a4 % _ g; d M l-M (yi NADA 3 Yr /= s y m \\u w-v ry-Q D P L m 5sL Q w, ' / u_ , y ~ M J -~-) -b ~ ?] = 5 j .P / 1 \\\\ N-a t- }\\ j $s. D l %e o E 3 4-y H' \\,? E O S-e SCALE OF WILES 5-2 -+ 20 's, LAKE "' 2 -2 o 43280 4 8 - s n. y

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A D l g DRgQwyER/ SURFACE WATER Q V2.VE VIch!GAN _.. /'I BAT 's, O WILK OHIO 4 TOLED =* I sv s' TAT ON N j [ K J H "EE" '"*" * "*'E5' ER i

FIGURE 3 0-3 3 0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SUPPLEMENTARY TLD LOCATIONS - BY STATION NUMBER' , 360N 4 [ f Ic. esse Iwa ance.R S-29,l / z" i N o ) "S-27 O t ONTAR10 3r O w m .n== CANADA ) A /,.)5-26 " a si. s ( I b 6 sw:r.: 1 / c,attT> Sk d ~ L j,g ~ 3 g I 3 g ~ _4h3 / t i

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) u uo 3% S- - U L ~ t 27031 ERWI 2 P.P.

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+*f h 2 0/ / 7 EO 'N, / S-14 6 s $?74[, ,' N, 'N o l ~ $_-2 S 12 \\

w

~~ N, / ~ /s .omot O 1 2 3 4 5 Y'., N N' F 's LEGEND 7;;' S 20 -2 / 'g $ N${hO$ ERIE' \\ ARTICULATES / a FISH AND/OR SEDIMENT ') A DRINKING WATER / SURFACE WATER g a D WATER // - 5-21 g j c FIGURE 3 .7 S llkNOTE jj sv STATION NuusER SAMPLING LOCATIONS K { H I (LESS THAN 10 MILES) b TE HA w E SEEFIO.2]{ ' { rOR LESS THAN 10 WILES. SEE FIG 3. s. a 4 _ ___ - = _ ____ :___

m j 3.2. INTERLABORATORY COWARISON PROGRAM DESCRIPTION The REW Contractor is required to participate in a Ccanission approved Interlaboratory Ccaparison Program and to sthmit QA Program Progress sunmary reports to DECO on a bi-monthly or quarterly basis. These reports contain susnary descriptions and performance data sunmaries on reference standards, bAank, blind, spiked, and dtplicate analyses as well as the USEPA and other 1poratory'* Interccuparison Programs, as applicable. A sumnary of the Interlaboratory Conparison Program results obtained is required to be included in the Annual Radiological Envircrvnental Operating Report pursuant to Specification 6.9.1.7. Participation in an approved Interlaboratory Ccnparison Program ensures that an independent check on. the precision and accuracy of the measurements of radioactive material in environmental sample matrices is performed as part of the QA program for environmental monitoring in order to domcristrate that the results are valid for the purpose of Section IV. B.2 of Appendix I to 10 CFR Part 50. ) 00CM, Fermi-2 3.0-10 2767W/0051W, 05/24/84 i

7 SECTION 4. TOTAL DOSE FROM URANIlN FLEL CYCLE 4 k CALCULATION OF TOTAL DOSE FROM URANIlN FLEL CYCLE sg In the event that calculations of total dose from the uranlun fuel cycle are required to be performed in stpport of the action statement 3.11.4.a as a result of exceeding twice the referenced limits, a combination of measurements will be incorporated. Direct radiation doses will be inferred from the evaluation of environmental monitoring devices (e.g., thermoluninescent dosimeters or ion chambers listed in Table 3.0-1). This component will be sumned with the doses calculated from effluents dose calculations perfomed according to Sections 1.0 and 2.0 of the 00CM to assess the annual dose or dose committment to any Member of the PLblic. e -4 00CM, Femi-2 4.0-1 3171W/0051W, 05/07/84}}