Text

Draft Offsite Dose Calculation Manual
	ML20080E846
Person / Time
Site:	Fermi
Issue date:	11/30/1982
From:	; DETROIT EDISON CO.
To:	;
Shared Package
ML20080E841	List: ML20080E838; ML20080E846;
References
	PROC-821130, NUDOCS 8402100174
	Download: ML20080E846 (78)
	v • d • e

, . _ _ - - . - _ - -

J

,/

1 j

d t

DRAFT 8 0FFSITE DOSE CALCULATION MANUAL for THE DETROIT EDISON COMPANY ENRICO FERMI ATOMIC POWER PLANT - UNIT 2 1

A November 1982 i

.i l

f 8402100174 840206 PDRADOCKOtDOO4}

A

u TABLE OF CONTENTS 1 l

PBQe List of Tables ........................... 11 Li s t o f Fi gu re s . . . . . . . . . . . . . . . . . . . . . . . . . . . 111 References ............................. iv Introduction ............................ v 1.0 LIqJIDEFFLUENTS 1.1 Liquid Effluent Monitor Setpoints ............. 1.0-1 1.1.1 Liquid Radwaste Effluent Line Hondor . . . . . . . . . 1. 0-1 1.1.2 Circulating Water Reservoir Decant Line Monitor . . . . 1.0-6 1.1.3 General Service Water Effluent Line Monitor . . . . . . 1.0-7 1.2 Dose Calculation for Liquid Effluents ........... 1.0-9 1.2.1 Duse to Critical Feceptor Due to Fish Consumption . . . 1.0-9 1.2.2 Dose Due to Fish and Drinking Water Consmption . . . . 1.0-11 1.3 Definitions of Liquid Effluent Terms . . . . . . . . . . . . 1.0-21 1.4 Liquid Radwaste Treatment System . . . . . . . . . . . . . . 1.0-25 2.0 GASEOUS EFFLUENTS 2.1 Gaseous Effluent Monitor Setpoints . . . . . . . . . . . . . 2. 0-1 2.1.1 Reactor Building Exhaust Plenm, Standby Gas ..... 2.0-1 TreatmentSystem, Radwaste Building Ventilation, and Turbine Building Ventilation 2.1.2 Containment Drywell Purge . . . . . . . . . . . . . . . 2.0-3 2.2 Gaseous Ef fluent Dose Calculations . . . . . . . . . . . . . 2.0-6

2. 2.1 Unrestricted Area Boundary Dose Rate ......... 2.0-6 2.2.2 threstricted Area Air Dose and Dose to Individual . . . 2.0-7 2.3 Meteorological Model . . . . . . . . . . . . . . . . . . . . 2.0-17 2.3.1 Atmospheric Dispersion ................ 2.0-17 2.3.2 Relative Deposition . . . . . . . . . . . . . . . . . . 2.0-20 1

2.4 Definitions of Gaseous Effluents Parameters ........ 2.0-31 i 2.5 Gaseous Radwaste Effluent System . . . . . . . . . . . . . . 2.0-36 3.0 RADIOLOGICAL ENVIR0tNENTAL MONITORING 3.1 Sampling Locations . . . . . . . . . . . . . . . . . . . . . 3.0-1 1

0D04, Fermi-2, Detroit Edison Company 1810W/0051W i

LIST OF TABES Table No. _Page No.

1.2-1 Bioaccumulation Factors 1.0-14 1.2-2 Adult Ingestion Dose Factors 1.0-15 1.2-3 SiteRelatedIngestionDoseCommitmentFactor(g7) 1.0-17 (Fish Consumption) I d

1.2-4 Site Related Ingestion Dose Commitment Factor (A'it) 1.0-19 (Fish and Water Consumption) 2.1-1 Dose Factors for Exposure to a Semi-Infinite Cloud of Noble Cases 2.0-5 2.2-1 Pathway Dose Factors for Section 2.2.1.b (Pg ) 2.0-10 2.2-2 Pathway Dose Factors for Section 2.2.2.b (Rg ) 2.0-14 2.3-1 Open Terrain Recirculation Factor 2.0-21 3.0-1 Environmental Radiological Sampling Locations 3.0-2 3.0-2 Supplementary TLD Stations 3.0-5 f

l l

l ODCN, Fermi-2, Detroit Edison Company l

1810W/0051W 11 L _ _ - _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ . _- -

LIST OF FIGURES Ficure No. Page No.

1.0-1 Example Calibration Curve for Liquid Effluent Monitor 1.0-8

1. 4-1 Liquid Radioactivity Monitoring System 1.0-26 2.3-A Vertical Standard Deviation of Material in a P1me (az ) 2.0-22 2.3-2 P1me Depletion Effect for Ground Level Releases 2.0-23 2.3-3 # Plume Depletion Effect for 30-m Releases 2.0-24 2.3-4 Plume Depletion Effect for 60-e Releases 2.0-25 2.3-5 Plume Depletion Effect for 100-m Releases 2.0-26 2.3-6 Relative Deposition for Ground-Level Releases 2.0-27 2.3-7 Relative Deposition for 30-m Releases 2.0-28 2.3-8 Relative Deposition for 60-m Releases 2.0-29 2.3-9 Relative Deposition for 100-m Releases 2.0-30 2.5-1 Gaseous Radwaste Effluent Monitoring System 2 0-37 3.0-1 Radiological Monitoring Program - Direct and Airborne 3.0-3 Measurements 3.0-2 Radiological Monitoring Program - Envirorsnental Samples 3.0-4 3.0-3 Radiological Monitoring Program - Supplementary TLD 3.0-6 Stations l

DDO4, Fermi-2, Detroit Edison Company 4 1810W/0051W 111 I i

- ~ 1

References Bellamy, L. Britz, and R. L. Waterfield ,

1. J. S. Boegli, R. R. W.

Specifications for

" Preparation of Radiological Effluent Technical Nuclear Power Plants", NUREG-0133 (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. NRC Regulatory Guide 1.109 (March 1976).

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

4. " Environmental Report, Operating License Stage", Detroit Edison Company, Fermi-2 Plant.

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

6. Methods for Estimating Atmospheric Transport and Dispersion of Gaseous Effluents in Routine Releases from L'ght-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, September 13, 1978.

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

l l

1 I

l l

0D04, Femi-2, Detroit Edison Company j 1810W/0051W

iJ i

INTRODUCTION The OFFSITE DOSE CALOJLATION manual is a supporting document of the RADIO-LOGICAL EFFLUENT TECWICAL SPECIFICATIONS. As such the ODW describes the methodo}ogy and parameters to be used in the calculation of offsite doses due to radioactive liquid and gaseous effluents and in the calculation of liquid and gaseous effluent monitoring instrtnentation alarm / trip setpoints. The ODW contains a list and graphical description of the specific sample loca-tions for the radiological environmental monitoing program. Schematic configurations of liquid and gaseous radwaste effluent systems releases to unrestricted areas are also included.

The ODN will be maintained at the plant for use as a reference guide and training document of accepted methodologies and calculations. Changes in the calculational methods or parameters will be incorporated into the 0D04 in order to assure that the ODCM represents the present methodology in all applicable areas. Computer softwart to perform the described calculations will be maintained current with the ODCM.

\

l 1

l i

ODm, Fermi-2, Detroit Edison Company v 181N/0051W

SECTION 1.

LIQUID EFFLUENTS l

l l

The Enrico Fermi Atomic Power Plant, Unit 2, is located on Lake Erie which ;

supplies make-up water to the Circulating Water System and receives decant l from the Circulating Water Reservoir. All releases from the Liquid Radwaste System are to the Circulating Water Reservoir decant line. Releases from the i General Service Water System are to the Circulating Water Reservoir. Although ;

no significant releases of radioactivity are expected from the General Service l Water System this effluent pathway is monitored as a precautionary measure.

1.1 LIQUID 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 be performed if the existing setpoint level corresponds to a lower count rate than the calculated value. The actual monitor setpoint, which corresponds to the calculated concentration plus background for the specific monitor, is determined from calibration data or from operational data associated with liquid sample analysis data. (See Section 1.1.1).

1 1.1.1 LIQUID RADWASTE EFFLUENT RADIATION LINE MONITOR D11 - N007 The liquid radwaste effluent line monitor provides alarm and automatic termination of release functions prior to exceeding the concentration limits l specified in 10CFR 20, Appendix B, Table II, Column 2 at the release point to !

the unrestricted area. To meet this specification, the alarm / trip setpoints for the liquid effluent monitor and flow measurement devices are set to assure that the following equation is satisfied:

cf <C (1)

F+f - MPC l

l 4

1 0D04, Fermi-2 1.0-1 1810W/0051W,11/06/82

QPC = the effluent concentration limit (Specification 3.11.1.1) implementing 10CFR 20 for the site, corresponding to the specific

( mix of isotopes in the effluent stream being considered for discharge, in pCIAnl.

c = the setpoint, in pCi/ml, of the radioactivity monitor measuring the radioactivity concentration in the effluent line prior to

, dilution and subsequent release; the setpoint, which is inversely proportional to the volunetric flow of the effluent line and pro-portional to the volumetric flow of the dilution stream plus the effluent stream, represents a value which, if exceeded, would I result in concentrations exceeding the limits of 10CFR 20 in the unrestricted area. l f = the flow setpoint as determined at the radiation monitor location, f in volune per unit time, but in the same units as F, below.

I F = the dilution water flow setpoint as determined prior to the release point, in volume per unit time.

At Fermi-2, the Liquid Radwaste System Waste Sample Tanks discharge to the Circulating Water Reservoir Oecant Line to Lake Erie. This decant line furnishes the dilution flow (F). The waste effluent flow (f) and the monitor setpoint (c) for the liquid radwaste pathway are determined and set to meet the conditions of equation (1) for a given effluent concentration, hPC*

The method by which this is accomplished is as follows:

Step 1) The isotopic concentration for a waste sample tank to be released is obtained from the sum of measured concentrations as determined by the analyses required in STS Table 4.11-1:

1 Ci= Cg + (Ca + Cs + Cr + Ct ) (2) where C

g

= the concentration Cg of each measured gamma emitter observed by l gamma-ray spectroscopy of each waste sample.

' 0004, Fermi-2 1.0-2 1810W/0051W,11/06/82

_ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ ~ _ _ _

I C, = the concentration of C, of alpha emitters in liquid waste as l measured in the MONTHLY composite sample. (NOTE: Sample is analyzed for gross a).

Cg e the measured concentrations of Sr-89 and Sr-90 in Jiquid waste as observed in the QUARTERLY composite sample.

C7 j= The measured concentrations of Fe-55 in liquid waste as observed in the QUARTERLY composite sample.

C = the measured concentration of H-3 in liquid waste as determined t '

from analysis of the MONTHLY composite sample, The C term will be included in the analysis of each batch; tems for alpha,

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

Step 2) The measured radionuclide concentrations are used to calculate a l

Dilution Factor, DF, which is the ratio of total dilution flow rate to tank flow rate required to assure that the limiting concentration of 10CFR 20, Appendix B, Table II, Column 2 are met at the point of discharge.

DF = 2 I + SF i MPCI C C C

= { o +f a+ s+ 7 . ti + SF (3) g MPCg MPCa MPC3 MPC7 MPCt where Cg = measured concentrations of C, g C,, C,, C 7

and C t

as defined in Step 1. Tems C, , C, C, and C "ill D' s 7 t included in the calculation as appropriate.

I i

0004, Fermi-2 1.0-3 1810W/0051W,11/06/82

- - - _ - - - _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ ]

,- i 1

MPCg MPC,, MPC,, MPC , and MPCg are limiting concentra-

=Mg, 7 tions of the appropriate radionuclide from 10CFR 20, Appendix B, !

Table II, Colmn 2. For dissolved or entrained noble gases, the l concentration shall be limited to 2 x 10 " pCiM1 total activity.

= the safety factor; a conservative factor used to compensate for SF 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, Fd '

, is established at ninety percent of the expected dilution flow rate: 1 F = (0.9) x (Circulating Water Reservoir N d

Decant Line Flow Rate.)

i Step 4) For the case DF < 1, the waste sample tank effluent concentration meets the limits of 10CFR 20 without dil:,: tion and effluent discharge flow rate may be assigned any desired value. For DF > 1, the maximum permissible discharge flow rate, tf , must be calculated:

F ft, Fd+Ip -

d for Fd >> fE (5)

DF F where:

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

calculations.

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

DF = Dilution Factor from step 2.

f = Flow rate of Waste Sample Tank discharge. (This value will have an p

upper limit of the maximum discharge capacity of the particular waste sample tank pe p.)

ODCM, Fermi-2 1.0-4 1810W/0051W,11/06/82

NOTE: If radioactivity from plant operations cccmulat:s in the Circulat-ing Water Reservoir such that measurable quantities of radio-nuclides vre detected in the Circulating Water Reservoir, calcula-tion of Fd must include a term to account for radioactivity present in the dilution stream prior to the introduction of the waste sample tank effluent:

F d

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

4 MPC fraction of Circulating Water Reservoir).

Step 5) The 11guld radwaste effluent radiation monitor setpoint may now be determined based on the values of { C1 , ft and Fd which were specified to provide compliance with the limits of 10CFR 20, Appendix B, Table II, Colmn 2. The monitor response is primarily to gamma radiation, therefore, the actual setpoint is based on g Cg . The 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[Cgdi. (6) g ml where A = Adjustment fector which will allow the setpoint to be established in a practical manner for convenie .ce and to prevent spurious alarms.

I

. t (See Note 2 below) (7) f(actual)

If A 11, Calculate c and determine the maximum value for the actual monitor setpoint (pCIAnl).

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

0004, Fermi-2 1.0-5 1810W/0051W,11/06/82 I - -

c

+

NOTE 1: The calculated setpoint concentration, c, establishes the base value for the monitor setpoint. However, in establishing 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 mest be controlled such that radioactivity levels in the offluent stream being monitored can

/ be accurately assessed at or below the calculated setpoint value.

I 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, a

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:

Liould Radwaste Effluent Radiation Monitor D11 - N007 Perform Step 2), solving equation (3) 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 setpoint should be established as close to background as practical to prevent spurious alams and yet alam should an inadvertent release occur.

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

l J

0004, Fermi-2 .

1.0-6 1810W/0051W,11/06/82

4 monitor has no control function, but serves cs support (backup) for the Liquid Radwaste Effluent Line Monitor and General Service Water System Monitor.

The radiation monitor setpoint is established as follows:

c=([C)+ 9 g DF (8)

~

where ICg and DF have values as detemined in Section 1.1.1 Step 1 and 0

Itep 2 respectively for the liquid radwaste sample tank planned for

release. i (For practicality, for this monitor only, if DF is determined to be < 1, OF may be set equal to 1 for the purpose of calculating the monitor setpoint.)

1.1.3 GENERAL SERVICE WATER MONITOR D 11 - N008 Concentration of radioactivity in this effluent line nomally is expected to be insignificant. Therefore, the monitor setpoint should be established as close to background as practical to prevent spurious alams and yet alam j should an inadvertent release occur.

If this effluent stream should become contaminated with radioactivity, radionuclide concentrations must be determined and a radiation monitor setpoint detemined as follows:

c = ( I C g) 4 DF (9) 9 where I Cg and DF are detemined using the sample analysis results for 9

this effluent stream and applying the methodology of Section 1.1.1 Step 1 and Step 2.

19 For this release pathway no additional dilution 4 aken t into account. -

Therefore, no releases are pemissible if DF > 1 ODCN, Femi-2 1.0-7 1810W/0051W,11/06/82

~ ' ~

- . - . - . .. . H~_-- .-. ~ inn -. _ . . . . .

4 FIGURE 1.0-1 EXAMPLE CALIBRATION CURVE FOR LIQUID EFFLUENT MONITOR

. . .. . . . .. . . . . . . . . . . . . }

t W l

=

k

+

3,- E1

.- 4i m-i 19' +

m S

D T.u

! ga *I M 'e c

E I l.

le' ;

ii T

3C' .

8

,7: y .c g l

se Eidi ..

iM 'a s; -

.=

l -

32 se' e 3 se ac 5 22' cm 0004, Fermi-2 1.0-8 1810W/0051W,11/06/82

7 1.2 DOSE CALCULATION FOR LIQUID EFFLUENTS t

For liquid dose calculations consideration is given to the two primary current flow patterns existing in the Lagoona Beach embayment of Lake Erie. The, maximm potential individual exposure is expected to exist with the current flow in the northerly direction and only the fish conseption pathway 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 intake for the city of Monroe makes it desirable to consider the wateIt conseption pathway as well as the fish consumption pathway.

The methodology for both cases is described in the following sections.

l i 1.2.1 DOSE TO CRITICAL RECEPTOR DUE TO FISH CONSLMPTION

- The dose contribution to the maximum exposed individual by way of fish consmption from all radionuclides identified in liquid effluents released to unrestricted areas is calculated using the following expression:

m -A t ic D = {A h [ Atg Cyg e Fg (10) i i=1 where D = The emulative dose commitment to the total body or any organ, T, due to radioactivity in 21 quid effluents for the total time period m

I att, in mrem (Reference 1).

i=1 at g = The length of the Eth time period over which Cyg and Fgare averaged for all liquid releases, in hours.

Cg = The average concentration of radionuclide, i, in undiluted liquid effluent during time period At g from any liquid release, in pCi/ml.

Ay = The decay constant for radionuclide 1. (sec.-1) l ODCM, Fertni-2 1.0-9 1810W/005W,11/06/82

t = The transit time to the location of the individual expected to c

receive the greatest potential dose due to the liquid pathway; 13,000 seconds. (Reference 5 Section 2.4.12).

Fg = The near field average dilution factor for Cyg during any liquid effluent release. Defined as the ratio of the undiluted 11g';1d waste flow during release to the product of the average flow j from the discharge structure to unrestricted receiving water times Z.

= (average undiluted liquid waste flow) (12)

(average flow from the discharge structure during periods of radioactive materials release) x (Z)

NOTE: The denominator of equation (12) is limited to 1000 cfs or less.

(Reference 1, Section 4.3).

where l Z = Applicable dilution factor for the receiving water body.

= 45 (Reference 1, Section 4.3; Reference 5, Appendix 11A,Section III.A.)

A h = The site related fish ingestion dose commitment factor to the total body or any organ T for each identified principal gamma and beta emitter listed in Table 1.2-3 in mrem-m1 per br-pCi.

Ah=K ($ BF ) DFg (11) where l

K g = Units conversion factor 1.14 x 10 5 l

106pCi x 10 m,1_

3

+ 8760 g pCi 1 yr S = Adult fish consumption (21 kg/yr).

OD04, Femi-2 1.0-10 1810W/0051W,11/06/82

[

BFy a Bloaccumulation factor for radionuclida 1, in fish, in pCi/kg per pCi/1 from Table 1.2-1 (taken from Reference 3, Table A-1).

DFy = Dose conversion factor for radionuclide 1, for adults in paselected organ, T, in mrem /pC1, from Table 1.2-2 (taken from l Reference 3, Table E-11).

If radioactivity in the Circulating Water Reservoir Decant Line becomes >

LLD, p;ior to the junction with the Liquid Radwaste Effluent Line, that concentration must be included in the dose determination. For this part of the dose calculation, Fg = 1 and at = the entire time period for which the dose is being calculated.

1.2.2 DOSE DUE TO FISH AND DRItKING WATER CONSLMPTION The dose contribution to an exposed individual by way of fish and drinking water consmption from all radionuclides identified in liquid effluents released to unrestricted areas is calculated using the following expression: ~

-A t m -A t

= A At gCgg e Ibg + A At gCyg e id (13)

D g7 F1 7 37 g }

i _ _ _

J where D = The cunulative dose commitment to the total body or any organ, T, 7

due to radioactivity in liquid effluents for the total time pericid m

I at ,t in mren (Reference 1).

i=1 at g = The length of the ith time period over which Cyg aM Fg are averagPd for all liquid releases, in hours.

Cyg = The average concentration of radionuclide, i, in undiluted liquid effluent during time period at g from any liquid release, in l

pCiAnl.

t Ag

= The decay constant for radionuclide i. (sec.~I) tg = The transit time to the location 1530n south of Fermi 2; 11,000 seconds. (Reference 5, Section 2.4.12) 00CM, Fermi-2 1.0-11 1810W/0051W,11/06/82 m -

'f t

d

= The transit time to the city of Monroe water intake; 23,000 seconds.

(Reference 5, Section 2.4.12)

F'g = The near field average ollution factor, at the location 1530n south of Femi-2, for Cyg during any liquid effluent release.

Defined as the ratio of the undiluted 11gJid waste flow during J. release to the product of the average flow from the discharge structure to unrestricted receiving water times Z'.

= (average undiluted liauid waste flow)

(average flow from the discharge structure during periods of radioactive materials release) x (Z')

NOTE: The denominator of equation (12) is limited to 1000 cfs or less.

(Reference 1, Section 4.3).

where Z' = Applicable dilution factor for the receiving water body at the location 1530n south of Femi-2.

= 67 (Reference 1, Section 4.3; Reference 5, Appendix 11A, Section i III.A.)

F"g = The near field average dilution factor, at the location of the city of Monroe drinking water intake, for Cyg during. any liquid

'~

effluer.t release. Defined as the ratio of the undiluted liquid waste flow during release to the product of the average flow from the discharge structure to unrestricted receiving water times Z".

F"t = (averaae undiluted liauid waste flow)

(average flow from the discharge structure during periods of radioactive materials release) x (Z")

where Z" = Applicable dilution factor for the receiving water body at the location of the city of Monroe drinking water intake.

0004, Fermi-2 1.0-12 1810W/0051W, 11/06/82- l L

2" = 77 (Reference 1, Section 4.3; Refercnce 5, App;ndix 11A, Section l III.A.)

= The site related drinking water ingestion dose commitment factor to A'h the total body or any organ T for each identified principal gamma and beta emitter listed in Table 1.2-4 in mrem el per br-pC1. j 4 ) DFy (14)

A'h

Ko(W where 5

K g

= Units conversion factor 1.14 x 10 3

106 DCi x 10 m_ l_ + 8760 hy_

pCi 1 yr

= Adult water consumption (730 liters / year).

4

= Dilution factor from the near field is within one-quarter mile of 3

the release point to the potable water intake for adult water consumption for Fermi 2 Plant, Dg = 1.

DFy = Dose conversion factor for nuclide 1, for adults in preselected organ, T, in mrem /pC1, from Table 1.2-2 (taken from Reference 3, Table E-ll).

Ag = See Section 1.2.1 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 the dose calculation, Fg = 1/Z, F'g = 1/Z', F"g = 1/Z" and et =

the entire time period for which the dose is being calculated.

0004, Fermi-2 1.0-13 1810W/0051W,11/06/82

TABLE 1.2-1 BIDACCUMULATION FACTORS (pCi/kg per pCi/ liter)*

FRESHWATER ELEMENT FISH H 9.0E-01 C 4.6E 03 NA 1.0E 02 P 1.0E 05 CR 2.0E 02 MN 4.0E 02 JE FE 1.0E 02 00 5.0E 01 NI 1.0E 02 00 5.0E 01 ZN 2.0E 03 BR 4.2E 02 RB 2.0E 03 SR 3.0E 01 Y 2.5E 01 ZR 3.3E 00 NB 3.0E 04 MO 1.0E 01 TC 1.5E 01 RU 1.0E 01 RH 1.0E 01

. TE 4.0E 02 I 1.5E 01 CS 2.0E 03 BA 4.0E 00 LA 2.5E 01 CE 1.0E 00 PR 2.5E 01 ND 2 5E 01 W 1.2E 03 NP 1.0E 01

! i

' Values in Table 1.2-1 are taken from Reference 3, Table A-1. 1 I

l l

l l 00CM, Fenni-2 1.0-14 1810W/0051W,11/06/82 j 1

TABLE 1.2-2 Page 1 of 2 ADULT INGESTION DOSE FACTORS *

(mrem /pCi ingested)

NuCL II;E AONE L I VE R T.ROGY TNTROIO EIDMEY LUNC CI-LLI et 3 NO DATA t.35E-07 8.CSE-07 1.'05E-07 I.05E-07 1.05E.07 1.05E-07

C 14 2.84E-06 5.68E-07 5.68E-07 5.68E-07 5.68E-07 5.A8E-07 5.68E-07 NA 24 1.70E-06 1.70E-06 t.70E-06 1. TOE-06 1.70E-06 1. TOE-06 8.70E-06 Pf 32 1.93E.04 1.20E-05 7.46E-06 NO DATA NO DATA NO DATA 2'.17E-05 Ct 5t NO DATA NO CATA 2.66E-09 1.59E-09 5.86E-to 3.53E.09 6.69E-07

NN 54 No DATA 4.57E-06 8. 72 E -0 7 NO DATA 1 36E-06 NO DATA 1 40E-05 MN $6 NO DATA 1.tSE-07 2.04E-08 ho DATA 1.46E-07 NO DATA 3.67E-c6 ft 55 2.75E-06 t.90F-06 4.4 J E-0 7 NO DATA NO DATA. 1.06E-06 1.09E-06 FE 59 4.34E-06 1 02E-05 3. 9 t E-0 6 90 DATA NO DATA 2.85E-06 3.40E-05 CO 58 NO DATA 7.456-07 1.67E-06 NO DATA NO DATA ND DATA 1 5tE-05 CO 40 NO DATA 2.14F-06 4.72C-06 NO DATA NO DATA NO DATA 4.02E-05 NI 63 1.30E-C4 9.01E-06 4.36E-06 NO DATA NO DATA NO DATA 1 88E-06

-- NI 65 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 3.9tE-08 NO DATA 2.10E-07 NO DATA 7.10E-06 2N 65 4.84E-06 1.542-05 6. 9 6 E -0 6 NQ DATA 1.03E-05 NO DATA 9.70E-06 2N 69 1.03E-08 1.97E-08 1. 3 7 E-0 9 NO DATA 1.28E-08 NO DATA 2.96E-09 em 83 NO DATA NO DATA 4. 02 E-0 8 NO DATA NO DATA NO DATA 5.79E-08 SR 84 NO DATA NO DATA 5.2tE-08 NO DATA NO DATA NO DATA 4.09E-13 SR 85 NO DATA NO DATA 2.14 E-0 9 NO DATA NO DATA NO DATA LT E-24 R8 86 NO DATA 2.1tE-05 9. 8 3 E-0 6 NO DATA NO O&TA NO DATA 4.16E-06 48 88 NO DATA 6.05E-08 3.2tE-08 NO DATA NO DATA NO DATA 8.36E-19 l ..................____...___.. ....._...__________..........._............ .

R8 89 NO DATA 4.01E-08 2.82C-08 NO DATA NO DATA NO DATA 2.33E-21' SR 89 3.08E-04 NO DATA 8. 8' E-0 6 NO DATA NO DATA NO DATA 4.94E-05 SR 90 7.58E-03 NO DATA 1.86E-03 NU OATA NO DATA NO DATA 2.19E-04 54 91 5.67E-06 NO DATA 2.29E-0 7 NO DATA NC DATA NO DATA 2.70E-05 SR 92 2.15E-06 NO DATA 9. 3 0 E-0 8 NO DATA NO DATA NO DATA 4.26E-05 Y 90 9.62E-09 NO DATA 2 58E-10 NO DATA No DATA NO DATA 1.02E-04 Y 9tN 9.09E-It NO DATA 3.52E-12 NO DATA NO DATA NO DATA 2.67E-to Y 91 1.4tE-0J NO DATA 3. 7 7E-0 9 NO DATA NO DATA NO DATA 7.76E-05 Y 92 8.45E-10 NO CATA 2.47E-11 NO DATA NO DATA NO DATA 1.68E-05 Y 93 2.68E-C9 NO DATA 7.40E-11 NO DATA NO DATA NO DATA 8.50E-05' ZR 95 3.04E-08 9.75E-09 6. 6 0 E-0 9 NO DATA 1.53E-08 NO DATA 3.09E-05 l ZR 97 t.68E-09 3.39E-10 1 55 E-10 NO DATA 5.12E-10 NO DATA 1.0$E-04 1 N8 95 6.22E-09 3.46E-09 1. 86 E-0 9 NO DATA 3.42E-09 No DATA 2.10E-05 MO 99 NO DATA 4.3tE-06 8. 2 0E-0 7 t40 D A T A 9.76E-06 N3 DATA 9.99E-06 TC 99M 2.47E-10 6.98E-10 8.89E-09 NO DATA 1.06E-08 3.42E-10 4 13E-07 TClot 2.54E-10 3.66E-to 3. 5 9 E -0 9 NO DATA 6.59E-09 1.87E-10 1.10E-21 auto) 4.85E-07 NO DATA 7.9fE-08 NO DATA 7.06E-07 NO DATA 2.16E.05 Rut 05 1.54E-08 No cATA 6.08E-04 No DATA t.99E-07 No DATA 9.42E-06

Values in Table 1.2-2 are taken from Reference 3, Table E-ll.

ODCM, Femi-2 1.0-15 181W/0051W,11/06/82

_--_ _l l TABLE 1.2-2 (Continued)

Page 2 of 2 i

E10NEY LuMC Cl-LLI l NuCLIOE CONE Liven T.600v TNv401C ;

5.3tt-06 No DATA t.7st-04 2u106 2.FSE-06 NO DATA 3. 4 s t-0 7 NO OtrA 6.04E-05 AC110n I.60E-07 1.4eE-07 0.79E-Os 40 DATA 2.9E-07 NO DATA

3. 59 E-0 7 0.06E-07 1.09E-05 No DATA t.0FE-05 l 2.6SE-06 9.7tE-07 ___...____.. i dEt25m_...._____...____..___________________________.._____.______.. NO DATA 2.2FE-05 I TE12fr 6.77E-06 2.42E-06 a . 2 5 E -0 7 1.73E-06 2.75E-05 NO DATA s.68E-06 TEt27 1.10E-0F 3.95E-08 2.3sE-Og e.15E-os 4.4eE-07 NO DATA 5.79E-05 TE129M 1.15E-05 4.29E-06 1.A2E-06 3 95E-06 4.80E-05

...__...___._..._................ ._..._____._.t.32E-0T ..........._._-......._____

NO DATA 2.37E-os TEt29 3.14E-08 1 18E-Os 7. 6s t-0 9 2.4tE-00 's . 4 0 E-0 5 t.34E-06 8.57E-06 NO DATA TEt3tm 1.73E-06 8.46E-07 7.05E-0 7 NO DATA 2.79E-09 ;

1.97E-C8 8.23E-09 6 . 22 E -0 9 1.62E-Os S.63E-06 FEt31 ;

______________.______.......______....______ ...___________ NO DATA

._____....... 7.7tE-05 __ '

IE132 2.52E-06 1.63E-06 1.53E-06 1.80E-06 1.57E-Q) !

2.2 3E-06 3.48E-06 NO DATA 1.92E-06 I 130 7.56E-07 0. 4 0E -0 7 1 09E-04 NO DATA 1.57E-06 t 131 4.16E-06 5.95E-06 3. 4 t E-0 6 1.95E-03 1.0ZE-OS 1.90E-07 t .'9 0 E-0 5 s.65E-07 NO DATA 1.02E-07 8 132 2.03E-07 5.43E-07 N0'0ATA 2.22E-06 )

8 133 1.42E-06 2.4FE-06 7.53E-07 3.63E-04 4.3tE-06 1.03E-07 4.99E-06 4.58E-07 NO DATA 2.51E-10 i I 134 1.06E-07 2.88E-07 j

...__.....__...____.________ ___.___.__..__.____ __...__.__.__...._____. NO DATA 1.3tE-06 t 835 4.43E-07 1.16E-06 4.2SE-07 7.65E-05 1.86E-06 1.48E-04 1.21E-04 NO DATA 4.79E-05 1.59E-05 2 59E-06 i C5134 6.22E-05 6.5tE-06 2.57E-05 1.85E-05 NO DArA 1.43E-05 1.96E-06 2.92E-06 C5136 C513T 7.97E-05 1.09E-04 7.14E-05 No DATA 3.70E-05 1.23E-05 2.ttE-06 s.01E-08 7.9tE-09 4.65E-13

) C513e 5.52E-08 1.09E-07 5.40E-08 NO DATA 1.72E-07 6.9tE-11 2. s 4 E-0 9 'NO DATA 6.46E-tt 3.92E-tt

. sat 39 9.70E-08 ._ -

sat 40 2.03E-05 2.551-08 1.33E-06 40 DATA 8.67E-09 1.46E-08 4.18E-05 4.FIE-08 1.56E-11 1.59E-09 NO DATA 3.31E-It 2.02E-Il 2.22E-17 P.A141 1.00E-26 2.13E-08 2.19E-11 1.34E-09 NO DATA t.35E-Il 1.24E-tt 4A142

...__.___...___.________._____....._______.____.___...____................__ 9.25E-05 2.50E-09 1.26E-09 3.3JE-10 NU OATA NO DATA NO DATA LAt40 4.25E-07 1.28E-10 1.4 5 E-11 NO DATA NO DATA NO DATA Lat42 5.82!-11 2.42E-05 CE141 9.36E-09 6.J3E-09 7.taE-10 NO DATA 2.94E-09 NO DATA 1.22E-06 1.35E-to NO DAT4 5.37E-10 NO DATA 4.56E-05 CEI43 1.65E-09 NO DATA 1.65E-04 CEt44 4.A8E-07 2.04E-07 2.62E-08 NO DATA t.2tE-07 3.69E-09 4.56E-to NU DATA 2 13E-09 NO DATA 4.03E-05 P4143 9.20E-09 ~

3.01E-11 1 25E-11 1.5sE-12 NO DATA 7.05E-t2 NO 047A 4.33E-18 l PRI44 3 49E-05 7.27E-09 4. 35 E -10 NO DATA 4.25E*09 NO DATA N0147 6.29E-09 NO DATA 2.82E-05 w 197 1.03E-07 8.6tE-04 3.01 E-0 5 NO DATA NO DATA

)

_.......______._....._______...._____________ ..________.._______ ..________ 2 40E-05 fir 2 39 1.19E 1.17E-10 6. 4 5E -1 1 ND DATA 3.65E-10 NO DATA l

Values in Table 1.2-2 are taken from Reference 3, Table E-11. -

1 0D04, Fermi-2 1.0-16 1810W/0051W,11/06/82 1

l

I TABLE 1.2-3 Pagn 1 of 2 SITE RELATED INGESTION DOSE COMMITMENT FACTOR, Ag (FISH CONSLNPTION)

(mrsn/hr per pCiAnl)

LIVER T. BODY THYROID KIDHEY LUNG GI-LLI HUCL1DE BONE 0.00E+00 2.26E-01 2.26E-01 2.26E-01 2.26E-01 2.26E-01 2.26E-01 H-3 14 3.13E+04 6.26E+03 6,26E+03 6.26E+03 6.26 +03 6.26E+03 6.26E+03 E

Ha b.4 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+06 Hn-56 0.00E+00 1.10E+02 1.K5E+01 0.00E+00 1.40E+02 0.00E+00 3.51E+03 Fe-55 6.58E+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+03 Co-60 0.00E+00 2.56E+02 5.65E+02 0.00E+00 0.00E+00 0.00E+00 4.81E+03

- Hi-63 3.11E+04 2.16E+03 1.04E+03 0.00E+00 0.00E+00 0.00E+00 4.50E+02 Hi-65 1.26E+02 1.64E+01 7.49E+00 0.00E+00 0.00E+00 0.00E+00 4.17E+02 Eu-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. 6 4 E + 08-Zn-69 4.93E+01 9.43E+01 6.56E+00 0.00E+00 6.13E+01 0.00E+00 1.42E+0!

Ir-S3 0.00E+00 0.00E+00 4.04E+01 0.00E+00 0.00E+00 0.00E+00 5.82E+0!

Ir-84 0.00E+00 0.00E+00 5.24E+01 0.00E+00 0.00E+00 0.00E+00 4.11E-Oo Ir-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+0o Fb-88 0.00E+00 2 90E+02 1.54E+02 0.00E+00 0.00E+00 0.00E+00 4.00E-09 j

Fb-89 0.00E+00 1.92E+02 1.35E+02 0.00E+00 0.00E+00 0.00E+00 1.12E-13 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 Sr-91 4.07E+02 0.00E+00 1.64E+01 0.00E+00 0.00E+00 0.00E+00 1.94E+03 Sr-92 1.54E+02 0.00E+00' 6.68E+00 0.00E+00 0.00E+00 0.00E+00 3.06E+03 Y-90 5.76E-01 0.00E+00 1.54E-02 0.00E+00 0.00E+00 0.00E+00 6.10E+03 Y-915 5.44E-03 0.00E+00 2.11E-04 0.00E+00 0.00E+00 0.00E+00 1.60E-02

%-91 8.44E+00 0.00E+00 2.26E-01 0.00E+00 0.00E+00 0.00E+00 4.64E+03 4-92 5.06E-02 0.00E+00 1.48E-03 0.00E+00 0.00E+00 0.00E+00 8.86E+02 Y-93 1.60E-01 0.00E+00 4.43E-03 0.00E+00 0.00E+00 0.00E+00 5.09E+03 2r-95 2.40E-01 7.70E-02 5.21E-02 0.00E+00 1.21E-01 0.00E+00 2.44E+02 2r-97 1.33E-02 2.68E-03 1.22E-03 0.00E+00 4.04E-03 0.00E+00 8.30E+02 Ub-95 4.47E+02 2.4SE+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 1c-99m 8.87E-03 2.51E-02 3.19E-01 0.00E+00 3.81E-01 1.23E-02 1.48E+01 Tc-101 9.12E-03 1.31E-02 1.29E-01 0.00E+00 2.37E-01 6.72E-03 3.95E-1C 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 1.46E-01 0.00E+00 4.75E+00 0.00E+00 2.26E+02_

l Calculated using Equation (11) 0004, FeIni-2 1 0-17 1810W/0051W, 11/06/82 l

TABLE 1.2-3 (Cbntinued)

Pag 3 2 of 2 LIVER T.PODY THYROID K1DHEY LUNG GI-LLI__

NUCL1DE BONE !

8.33E+00 0.00E+00 1.27E+02 0.00E+00 4.26E+03 Fu-106 6.58E+01 0.00E+00 Ag-110m 8.81E-01 8.15E-01 4.84E-01 0.00E+00 1.60E+00 0.00E+00 3.33E+02 1.04E+04 0.00E+00 1.02E+0c Te-125m 2.57E+03 9.30E+02 3.44E+02 7.72E+02 0.00E+00 2.17E+0 Te-127m 6.48E+03 2.32E+03 7.90E+02 1.66E+03 2.63E+04 Te*127 1.05E+02 3.78E+01 2.28E+01 7.80E+01 4.29E+02 0.00E+00 8.31E+07 Te-129m 1.10E+04 4.11E+03 1.74E+03 3.78E+03 4.60E+04 0.00E+00 5.54E+0 Te-129 3.01E+01 1.13E+01 7.33E+00 2.31E+01 1.26E+02 0.00E+00 2.27E+0!

8.10E+02 6.75E+02 1.28E+03 8.21E+03 0.00E+00 8.04E+0c Te-131m 1.66E+03 0.00E+00 2.67E+00 Te-Wbt 1.89E+01 7.88E+00 5.96E+00 1.55E+01 8.26E+01 Te-132 2.41E+03 1.56E+03 1.47E+03 1.72E+03 1.50E+04 0.00E+00 7. 3 8 E + 0.-

I-130 2.71E+01 8.01E+01 3.16E+01 6.79E+03 1.25E+02 0.00E+00 6.89E+0!

I-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 1-134 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+0!

Cs-134 2.98E+05 7.09E+05 5.79E+05 0.00E+00 2.29E+05 7.61E+04 1.24E+0 Cs-136 3.12E+04 1.23E+05 8.86E+04 0.00E+00 6.85E+04 9.38E+03 1.40E+0' 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 En-139 9.29E-01 6.62E-04 2.72E-02 0.00E+00 6.19E-04 3.75E-04 1.65E+00 La-140 1.94E+02 2.44E-01 1.27E+01 0.00E+00 8.30E-02 1.40E-01 4.00E+02 La-141 4.51E-01 3.41E-04 1.52E-02 0.00E+00 3.17E-04 1.93E-04 2.13E-10 La-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-62 1.99E-02 0.00E+00 0.00E+00 0.00E+00 5.54E+0?

La-142 7.66E-03 3.48L-03 ,8.68E-04 0.00E+00 0.00E+00 0.00E+00 2.54E+0!

Ce-141 2.24E-02 1. 5 2 E 1.72E-03 0.00E+00 7.04E-03 0.00E+00 5.79E+01 3

Ca-143 3.95E-03 2.92E+00 3.23E-04 0.00E+00 1.29E-03 0.00E+00 1.09E+02 Cs-144 1.17E+00 4.88E-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+07 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 S.65E+01 0.00E+00 0.00E+00 0.00E+00 8.10E+0 Np-239 2.E5E-02 2.80E-03 1.54E-03 0.00E+00 S.74E-03 0.00E+00 5.75E+0P.

Calcuated using Equation (11) 0D04, FeI1ni-2 1.0-18 1810W/0051W,11/06/82

TABUE 1.2-4 Paga 1 of 2 l

s SITE RELATED INGESTION 00SE CDe4ITMENT FACTOR, A'iT (WATER CONSLMPTION)

! (mrem /hr per pCI Anl) l l I l f NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI 1 j H-3 0.00E+00 8.74E+00 8.74E+00 8.74E+00 8.74E+00 8.74E+00 8.74E+00 ;

C-14 2.36E+02 4.73E+01 4.73E+01 4.73E+01 4.73E+01 4.73E+01 4.73E+01 '

Ha-f4 1.41E+02 1.41E+02 1.41E+02 1.41E+02 1.41E+02 1.41E+02 1.41E+02 P - T. 1.61E+04 9.99E+02 6.21E+02 0.00E+00 0.00E+00 0.00E+00 1.81E+03 i Cr-51 0.00E+00 0.00E+00 2.21E-01 1.32E-01 4.88E-02 2.94E-01 5.57E+01 Mn-54 0.00E+00 3.80E+0i 7.26E+01 0.00E+00 1.13E+02 0.00E+00 1.17E+00 Hn-56 0.00E+00 9.57E+00 1.70E+00 0.00E+00 1.22E+01 0.00E+00 3.05E+02 Fe-55 2.29E*02 1.58E+02 3.69E+01 0.00E+00 0.00E+00 8.82E+01 9.07E+01 Fe-59 3.61E+02 8.49E+02 3.25E+02 0.00E+00 0.00E+00 2.37E+02 2.83E+03

! Co-58 0.00E+00 6.20E+01 1.39E+02 0.00E+00 0.00E+00 0.00E+00 1.26E+03

Co-60 0.00E+00 1.78E+02 3.93E+02 0.00E+00 0.00E+00 0.30E+00 3.35E+03 Hi-63 1.08E+04 7.50E+02 3.63E+02 0.00E+00 0.00E+00 0.00E+00 1.56E+02 3

Hi-65 4.39E+01 5.71E+00 2.60E+00 0.00E+00 0.00E+00 0.00E+00 1.45E+02

. Cu-64 0.00E+00 6.93E+00 3.25E+00 0.00E+00 1.75E+01 0.00E+00 5.91E+02 2n-65 4.03E+02 1.28E+03 5.79E+02 0.00E+00 8.57E+02 0.00E+00 8.07E+02 2n-69 8.57E-01 1.64E+00 1.14E-01 0.00E+00 1.07E+00 0.00E+00 2.46E-01 1.r- 8 3 0.00E+00 0.00E+00 3.35E+00 0.00E+00 0.00E+00 0.00E+00 4.82E+00 Ir-84 0.00E+00 0.00E+00 4.34E+00 0.00E+00 0.00E+00 0.00E+00 3.40E-OS Ir-85 0.00E+00 0.00E+00 1.78E-01 0.00E+00 0.00E+00 0.00E+00 8.32E-17 Fb-86 0.00E+00 1.76E+03 8.18E+02 0.00E+00 0.00E+00 0.00E+00 3.46E+02 Fb-88 0.00E+00 5.03E+00 2.67E+00 0.00E+00 0.00E+00 0.00E+00 6.96E-11

) Rb-89 0.00E+00 3.34E+00 2.35E+00 0.00E+00 0.00E+00 0.00E+00 1.94E-13 i Sr-89 2.56E+04 0.00E+00 7.36E+02 0.00E+00 0.00E+00 0.00E+00 4.11E+03 Sr-90 6.31E+05 0.00E+00 1.55E+05 0.00E+00 0.00E+00 0.00E+00 1.82E+0c

Sr-91 4.72E+02 0.00E+00' 1.91E+01 0.00E+00 0.00E+00 0.00E+00 2.25E+03 Sr-92 1.79E+02 0.00E+00 7.74E+00 0.00E+00 0.00E+00 0.00E+00 3.55E+03 3 Y-90 8.01E-01 0.00E+00 2.15E-02 0.00E+00 0.00E+00 0.00E+00 8.49E+03 Y-91m 7.56E-03 0.00E+00 2.93E-04 0.00E+00 0.00E+00 0.00E+00 2.22E-02 i Y-91 1.17E+01 0.00E+00 3.14E-01 0.00E+00 0.00E+00 0.00E+00 6.46E+03

Y-92 7.03E-02 0.00E+00 2.06E-03 0.00E+00 0.00E+00 0.00E+00 1.23E+03

Y-93 2.23E-01 0.00E+00 6.16E-03 0.00E+00 0.00E+00 0.00E+00 7.07E+0?

! Ir-95 2.53E+00 8.11E-01 5.49E-01 0.00E+00 1.27E+00 0.00E+00 2.57E+03 2r-97 1.40E-01 2.82E-02 1.29E-02 0.00E+00 4.26E-02 0.00E+00 8.74E+03 bb-95 5.18E-01 2.8SE-01 1.55E-01 0.00E+00 2.85E-01 0.00E+00 1.75E+03 No-99 0.00E+00 3.59E+02 6.82E+01 0.00E+00 8.12E+02 0.00E+00 8.31E+02 1 c - 9 9 t.. 2.06E-02 5.81E-02 7.40E-01 0.00E+00 8.82E-01 2.85E-02 3.44E+01 Tc-101 2.11E-02 3.05E-02 2.99E-01 0.00E+00 5.48E-01 1.56E-02 9.15E-1' Fu-103 1.54E+01 0.00E+00 6.63E+00 0.00E+00 5.88E+01 0.00E+00 1.80E+03 Fu-105 1.2SE+00 0.00E+00 5.06E-01 0.00E+00 1.66E+01 0.00E+00 7.04E+02 Calculated using Equation (11)

C.D4, Fezini 1.0-19 1810ki/0051W,11/06/82

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

TABLE 1.2-4 (Continued)

Pag 2 2 of 2 k CLIDE BONE LIVER T.F0DY THYROID KIDNEY LUNG GI-LLI Ru-106 2.29E+02 0.00E+00 2.90E+01 0.00E+00 4.42E+02 0.00E+00 1.48E+0*-

Ag-y0m 1.33E+01 1.23E+01 7.32E+00 0.00E+00 2.42E+01 0.00E+00 5.03E+03 Te-n5m 2.23E+02 8.08E+01 2.99E+01 6.71E+01 9.07E+02 0.00E+00 8.90E+02 Te-127s. 5.63E+02 2.01E+02 6.87E+01 1.44E+02 2.29E+03 0.00E*00 1.89E+03 Te-127 9.15E+00 3.29E+00 1.98E+00 6.78E+00 3.73E+01 0.00E+00 7.22E+02 Te-129m 9.57E+02 3.57E+02 1.51E+02 3.29E+02 3.99E+03 0.00E+00 4.82E+03 Te-129 2.61E+00 9.82E-01 6.37E-01 2.01E+00 1.10E+01 0.00E+00 1.97E+00 Te-131m 1.44E+02 7.04E+01 5.87E+01 1.12E+02 7.13E+02 0.00E+00 6.99E+03 Te-131 1.64E+00 6.85E-01 5.18E-01 1.35E+00 7.18E+00 0.00E+00 2.32E-01 Te-132 2.10E+02 1.36E+02 1.27E+02 1.50E+02 1.31E+03 0.00E+00 6.42E+03 I-133 6.29E+01 1.86E+02 7.32E+01 1.57E+04 2.90E+02 0.00E+00 1.60E+02 1-131 3.46E+02 4.95E+02 2.84E+02 1.62E+05 8.49E+02 0.00E+00 1.31E+02 I-132 1.69E+01 4.52E+01 1.58E+01 1.58E+03 7.20E+01 0.00E+00 8.49E+00 1-133 1.18E+02 2.06E+02 6.27E+01 3.02E+04 3.59E+02 0.00E+00 1.85E+02 1-134 8.82E+00 2.40E+01 8.57E+00 4.15E+02 3.81E+01 0.00E+00 2.09E-02 I-135 3.69E+01 9.65E+01 3.56E+01 6.37E+03 1.55E+02 0.00E+00 1.09E+02 Cs-134 5.18E+03 1.23E+04 1.01E+04 0.00E+00 3.99E+03 1.32E+03 2.16E+02 Cs-136 5.42E+02 2.14E+03 1.54E+03 0.00E+00 1.19E+03 1.63E+02 2.43E+02 Cs-137 6.63E+03 9.07E+03 5.94E+03 0.00E+00 3.08E+03 1.02E+03 1.76E+02 Cs-138 4.59E+00 9.07E+00 4.49E+00 0.00E+00 6.67E+00 6.58E-01 3.87E-05

Fa-139 8.07E+00 5.75E-03 2.36E-01 0.00E+00 5.38E-03 3.26E-03 1.43E+01 Fa-140 1.69E+03 2.12E+00 1.11E+02 0.00E+00 7.22E-01 1.22E+00 3.48E+03 Fa-141 3.92E+00 2.96E-03 1.32E-01 0.00E+00 2.75E-03 1.68E-03 1.85E-09 Fa-142 1.77E+00 1.02E-03 1.12E-01 0.00E+00 1.54E-03 1.03E-03 2. 50E- 11:

La-140 2.08E-01 1.05E-01 2.77E-02 0.00E+00 0.00E+00 0.00E+00 7.70E+03 La-142 1.07E-02 4.84E-03 1.21E-03 0.00E+00 0.00E+00 0.00E+00 3.54E+01 Ce-141 7.79E-01 5.27E-01' 5.98E-02 0.00E+00 2.45E-01 0.00E+00 2.01E+03 Ce-143 1.37E-01 1.02E+02 1.12E-02 0.00E+00 4.47E-02 0.00E+00 3.79E+03 Ce-144 4.06E+01 1.70E+01 2.18E+00 0.00E+00 1.01E+01 0.00E+00 1. 3 7 E + 0'-

Fr-143 7.66E-01 3.07E-01 3.79E-02 0.00E+00 1.77E-01 0.00E+00 3.35E+03 Fr-144 2.50E-03 1.04E-03 1.27E-04 0.00E+00 5.87E-04 0.00E+00 3.60E-10 Nd-147 5.23E-01 6.05E-01 3.62E-02 0.00E+00 3.54E-01 0.00E+00 2.90E+03 L-187 8.57E+00 7.17E+00 2.50E+00 0.00E+00 0.00E+00 0.00E+00 2.35E+03 hp-239 9.90E-02 9.74E-03 5.3?E-03 0.00E+00 3.04E-02 0.00E+00 2.00E+03 0004, Fermi-2 1.0-20 1810W/0051W,11/06/82

l.3 DEFINITIONS OF LIQUID EFFLUENT TERMS Section of Term Definition Initial Use A = adjustment factor applied to facilitate setting actual 1.1.1 monitor setpoints.

Ag the site related ingestion dose commitment factor due 1.2 g

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-m1 per br-pC1.

= the site related ingestion dose commitment factor due to 1. 2. 2 A'h water and fish consunption to the total body or any organ T

~

for each identified principal gamma and beta emitter listed in Table 1.2-4 in mrem-m1 per br-pC1.

BFy = Bioaccumulation Factor for nuclide 1, in fish, pCi/Kg per 1. 2.1 pCi/1, from Table 1.2-1.

C = the effluent concentration limit (Specification 3.11.1.1) 1.1.1 MPC implementing 10CFR 20 for the site, in pCIAnl.

C, = the effluent concentration of alpha emitting nuclides 1.1.1 observed by gross alpha analysis of the MONTHLY composite sample.

C = The concentration of Fe-55 in liquid wastes as 1.1.1 7

observed in the QUARTERLY composite sample.

C = the effluent concentration of a gamma emitting nuclide, g, 1.1.1 g

observed by gamma-ray spectroscopy of the waste sample.

Cy = the concentration of nuclide i as detemined by the 1.1.1 analysis of the waste sample.

ODCM, Femi-2 1.0-21 1810W/0051W,11/06/82 l

a -- . -.,, , . . .

9 Section of Term Definition Initial Use Cyg = the average concentration of radionuclide, i, in undiluted 1.2.1 liquid effluent during time period att from any liquid release, in pCi Anl.

= the concentration of Sr-89 or Sr-90 in liquid wastes 1.1.1 C,

I as determined by analysis of the QUARTERLY composite sample.

C = the measured concentration of H-3 in liquid waste 1.1.1 as determined by analysis of the MONTHLY composite.

c = the setpoint of the radioactivity monitor measuring the 1.1.1 radioactivity concentration in the effluent line prior to dilution and subsequent release.

I DFg = a dose conversion factor for nuclide, i, for adults in 1. 2.1 preselected organ, T, in mrem /pCi found in Table 1.2-2.

l.

D = the ctanulative dose commitment to the total body or any 1.2.1 organ, T, from the liquid effluents for the total time period.

4 i

DF = the dilution factor, which is the ratio of the total 1.1.1 dilution flow rate to the effluent stream flow rate (s) f required to assure that the limiting concentration of 10CFR, Part 20, Appendix B, Table II, Column 2 are met at the point of discharge.

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 1.)

l F = the flow rate of the dilution stream used for setpoint 1.1.1 i d

calculations during the time of release, which is l (0.9) x actual dilution flow.

{

! ODCN, Fermi-2 1.0-22 1810W/0051W,11/06/82

ie Section of Definition Initial Use Term

= effluent flow rate 1.1.1 f

p

~

= the flow setpoint as determined for the radiation monitor 1.1.1 f

location. (Ceneral expression for equation 1.) .

4 1.1.1 f = maximum permissible effluent flow rate t

Fg = the near field average dilution factor for Cig during any 1.2.1 I liquid effluent release.

F'g = The near field average dilution factor, at the location 1530m south of Fermi-2, for Cyg during any liquid effluent release.

F"g

= The near field average dilution factor, at the location of the city of Monroe drinking water intake, for Cyg during any 11guld effluent r'elease.

e K = 1.14 x 10', units conversion factor. 1 2.1 i

MPC , MPC 1 1.1 MPCy g a , MPC s , MPC 7 , and MPQ

. - the limiting concentrations of the appropriate gamma emitting radionuclides, alpha emitting radionuclides, strontium, iron and tritium, respectively, from 10CFR, Part 20, Appendix B, Table II, Column 2.

SF r 4 m safety factor, a conservative factor used to compen- 1.1.1 sate for statistical fluctuations and errors of measure-ments.

t = the transit time to the city of Monroe water intake; , 1.2.2 d

23,000 seconds. (Reference 5, Section 2.4.12) 00CH, Fermi-2 1.0-23 1810W/0051W, 11/06/82

Section of Term Definition Initial Use t = The transit time to the location of the individual 12.1 c

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 1530n south of Fermi 2; 7

11,000 seconds. (Reference 5, Section 2.4.12)

At = duration of release under consideration. 1. 2.1 m = nunber of liquid releases. 1.2.1 UF = 21 kg/yr, fish consumptian (adult). 1.2.1

= adult water consumption, 7301/ year. 1 2.2 Z = Applicable factor when additional receiving water body 1.2.1 dilution is to be considered; Z = 45.

Z' = Applicable dilution factor for the receiving water body at the location 153On south of Fermi 2, Z=67.

Z" = Applicable dilution factor for the receiving water body at the location of the city of Monroe drinking water intake; Z=77.

A y

= The decay constant for radionuclide 1. (sec-1) 1. 2.1 i

ODCM, Fermi-2 1.0-24 1810W/0051W, 11/06/82

b l 1.4 LIQUID RADI0 ACTIVE MONITORING SYSTg ;

1 l

FIGRE 1.4-1 is a schematic of the Liquid Radwaste Monitoring System showing the release points to the unrestricted area.

\

l

}

DDCM, Femi-2 1.0-25 1810W/0051W,11/06/82

^

k j LIQUID RADWASTE' SYSTEM ,_ s - cgigm _,,

4 "a A, A T'" ;

7 m i cm m ) ( v b on=re V V V I ne , r=a ca<r.> -

. od il ya n

p [ omaa E7 gam A A

,ig, r=

L

.m

__a_-

m Q -E.

e' =u .m

~ I k tt#lm_ ; m i }

L)esa j-I nim mime 1 ge---

yx vg5..----4

.. V V D i a r -:t !

5'"

EE n h( 99 .

I Y Etti LLE 5

. on e 4 g .g = .-

l =r -

W W E 5 -

! f T O i .%v ;

i a T_ .

~~ ^

l j

e ERim Rl51 D

()k 0 '

i 1

/ _ _

ar. av.F \ f'

, - } . .m o{_ ~

lD

$0VI .TD j

M a,rr. f' ' riar$ t21 U(D gg g .,

(

"g g

c

= = x.

O y,

'x<= -

LIQUID RADIATION j

EFFLUENT qT -

MONITORING SYSTEM j i

. . ~

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.

If no release is planned for a particular pathway, the monitor setpoint should be established as close to background as practical to prevent spurious alams yet alarm should an inadvertent release occur.

If a calculated setpoint is less than the monitor reading associated with the particu ar 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, AND TURBINE BUILDING VENTILATION RADIATION MONITORS Monitors: D 11 - N407; D 11 - N406A and B; D 11 - N403; D 11 - N405; and D 11 - N404.

For the purpose of implementation of Technical Specification 3.3.7.12, the alarm setpoint level for theso noble gas monitors will be calculated as follows:

C 5

= monitor reading of the noble gas monitor at the alarm setpoint concentration.

(B x SF) x RtxDg (1)

= the lesser of or (B x SF) x Rs' x Dss (2) 0D04, Fermi-2 2.0-1 2611W/0051W, 11/05/82

SF a safety factor; o cons 0rvative factor Cpplicd to cach noble gas 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 release 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, B may be set equal to 1/n, where n is the number of simultaneous final gaseous release points.)

Dg = Dose rate limit to the total body of an individual which is 500 mrem / year.

R t

= monitor reading per mrem /yr to the total body

= C + (T/Q) [ Ki Qi) (3) 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. For batch releases the sample must be taken prior to release; for continuous releases the sample is taken during the release. The count rate corresponding to the measured concentra-tion is determined from the monitor calibration curve for the particular monitor.

X/Q = 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.)

S/C = 4.186 x 10-6 secAn3 in the NW sector.

00CM, Fermi-2 2.0-2 2611W/0051W,11/05/82

Kg o total body dose factor due to gamma emissions from isotope 1 (mrem /yr per pC1/m 3 ) from Tabic 2.1-1.

l Qg = rate of release of noble gas radionuclide 1 (pCi/sec) from the release pathway under consideration. The product of Xgy and F,y where X gy is the concentration of radionuclide i for the particular release volme and Fy is the release flowrate. (Xg in pC1/cc and F in cc/sec.)

y D,3 = Dose rate limit to the skin of the body of an individual in an unrestricted area which is 3000 mrem / year.

R s

= monitor reading per mrem /yr to the skin

= C + X/Q (Li + 1.1 M1 ) Qi (4)

Ly = skin dose factor due to beta emissions from isotope 1 (mrem /yr per pCi A 3) from Table 2.1-1.

1.1 = mrem skin dose per mrad air dose M

y = air dose factor due to gamma emissions from isotope 1 (mrad /yr per pCih ) from Table 2.1-1.

l 2.1.2 CONTAIW ENT DRYWELL PLRGE The containment Drywell Purge is a batch-type release which discharges to j 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

% wever, if a decision is made to route the discharge through the Reactor Building Exhaust Plenm, the setpoint for the Reactor Building Exhaust Plenum effluent monitor must be redetermined to account for the source term 0D04, Fermi-2 2.0-3 2611W/0051W,11/05/82

7 cssociat;d eith the drywell purge. This is cecomplished by following the methodology of Section 2.1.1, with the following exception:

Qg must be replaced with a new source term, Q y';

I where Q y ' = Qg+gg i

l j and where Ay = the drywell purge source term, which is the radicauclide concentration multiplied by the planned drywell purge release rate.

1 I

e i

l 0004, Fermi-2 2.0-4 2611W/0051W,11/05/82

~- ~

l

." l l

l TABLE 2.1-1 DOSE FACTORS FOR EXPOSURE TO A SEMI-INFINITE CLOUD OF NOBLE GASES

MJclide Y-Body'** (K) 6-Skin ***(L) y- Ai r* * (M ) B-Air **(N)

Kr-85m 1.17E + 03* * *

1.46E+03 1.23E+03 1.97E+03 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 1.06E+04 Kr-90 1.56E+04 7.29E+03 1.63E+04 7.83E+03 Xe-131m 9.15E+01 4.76E+02 1.56E+02 1.11E+03 Xe-133m 2.51E+02 9.94E+02 3.27E+02 1.48E+03 l Xe-133 2.94E+02 3.06E+02 3.53E+02 1.05E+03 Xe-135m 3.12E+03 7.11E+02 3.36E+03 7.39E+02 Xe-135 1.81E+03 1.86E+03 1.92E+03 2.46E+03 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

(

a mrad-e3 pCi-yr un mrem-m3 pCi-yr

- - - 1.17E+03 = 1.17 x 103 l

OOCM, Femi-2 2.0-5 l 2611W/0051W,11/05/82

2.2 GASEOUS EFFLUENT DOSE CALCULATIONS l

2.2.1 UtRESTRICTED AREA BOUNDARY DOSE RATE i 2.2.1.a Dose Rates Due to Noble Gases For the purpose of implementation of Technical Specification 3.ll.2.1.a the dose rate at the unrestricted area boundary due to noble gases shall be calculated as follows:

D = avercge total body dose rate in the current year (mrem /yr)

(5)

= (X/Q) f Ki Q)

- D = average skin dose rate in current. year (mrem /yr) s

= (X/Q) [ (Li+1.1M)Q) i (6) 1 (NOTE: terms defined previously in Section 2.1.1) 2.2.1.b Dose Rates Due to Radiciodines. Tritium, and Particulates Organ dose rates due to radiciodines, tritium, and all radioactive materials in particulate form with half-lives greater than eight days, will be calculated for the purpose of implementation of Technical Specification 3.11.2.1.b as follows:

Dg = average organ dose rate in the current year (mrem /yr)

=(X/Q)]Pi (T) (7)

L where '

X/Q = The highest annual average relative concentration in any sector at the site boundary (for values see Section 2.1.1). (The highest annual average or the annual average determined for the particular release point may be used.)

0D04, Fermi-2 2.0-6 1 l

2611W/0051W,11/05/82

Pg = dose parameter for radionuclide i, (mrem /yr per pCi/m ) for inhalation.

'( = The release rate of non-noble gas radionuclide i as determined from the concentrations measured in the analysis of the appropriate sample required by Technical Specifications 3.ll.2.1.b.

2.2.2 LNIESTRICTED AREA AIR DDSE Ato DOSE TO INDIVIDUAL 2.2.2.a Air 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 radionuclides (mrad)

= 3.17 x 10-8 M i(X/Q)(h) i (8) where 3.17 x 10-8 = the fraction of one year per one second

= cumulative release of noble gas radionuclide i over the period of Q1 interest (pC1) for the type of release under consideration.

D = air dose due to beta emissions from noble gas radionuclides (mrad).

= 3.17 x 10-8 [ Ni (X/Q)(Qi ) (9)

)

My = defined in Section 2.1.1 Ng = air dose factor due to beta emissions from noble gas radionuclide 1 3

(mrad /yr per pC1/m from Table 2.1-1).

(M) = 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 l

j may be used if desired.)

0004, Fermi-2 2.0-7 2611W/0051W,11/05/82 1

~ ~ ~ ~ ~ ~ ~ - ~ ~ - ~ ~

. . .. . _ . . ._ .._- . J. J_. _~ ~ T' 2.2.2.b Dose To An Individual In Unrestricted Area Dose to an individual from radiciodines, tritim and radioactive materials in l

1 particulate form will be calculated for the purpose of implementation of Technical Specifications 3.11.2.3 and 3.11.2.4 as follows:

D = dose to an individual from I-131, tritium, and radionuclides in p .

particulate form (mrem).

= 3.17 x 10-0 R(W')h')

i i (10) where W' = relative dispersion parameter for location of controlling receptor (The highest annual or grazing season average may be used; or the annual or grazing season average for the particular release point may be used if desired.)

(X/Q') for inhalation and all tritium pathways 2.686 E-7 sec/m3 in the WNW sector

= (D/Q') for other pathways 2.763 E-9 m-2 in the WNW sector (mrem /yr per pC1/m ) or (m 2 3

Rg = dose factor for radionuclide 1, _

mrem /yr per pCi/sec) from Table 2.2-2.

i' = cmulative release of radiciodine, tritim, or material in particuate form (required by Technical Specification 3.11.2.3) over the period of interest (pCi), for the type of release under consideration.

2. 2. 2.c Dose Calculations To Support Other Specific Technical Specifications )

For the purpose of implementing Technical Specification 6.9.1.13 dose 1 calculations will be performed using the equations in Section 2.2.2.b with the substitution of average meteorological parameters for the period of the l report, and the appropriate pathway receptor dose factors (R ). j ODCM, Fermi-2 2.0-8 l 2611W/0051W, 11/05/82

For the purpos2 of implem nting Technical Specification 6.9.1.9, dose calculations may be perfomed using the above equations with the substitution of the dispersion parameters (X/Q, D/Q) which are concurrent with actual releases, and the appropriate pathway receptor dose factors.

For the purpose of implementing Technical Specification 3.12.2, dose calcula-tions may be performed using the above equations substituting the appropriate pathway receptor dose factors and the appropriate dispersion parameters for the location (s) of interest. Annual average dispersion parameters (or grazing period average for D/Q) may be used for these calculations.

2.2.2.d Surnmation of Dose Rates and Doses For the purpose of implementing Technical Specification 3.11.2.1, dose rates due to simultaneous releases will be summed to assure that the dose rate limits at any point in time are not exceeded. For the purpose of implementing Technical Specification 3.11.2.2, the air doses from all gaseous release points will be summed to assure that the quarterly and annual limits are not exceeded. For the purpose of implementing Technical Specification 3.11.2.3, the organ doses to an individual will be sunmed to assure that the quarterly and annual limits are not exceeded.

t i

l ODO4, Fermi-2 2.0-9 2611W/0051W,11/05/82

TABLE 2.2-1 PATl4(AY DOSE FACTORS FOR SECTION 2.2.1.6 (P g )*

i (For Dose Calculation Required by TS 3.11.2.1)

I Page 1 of 4 4 AGE GROUP ( CHILD )

ISOTOPE : INHALATION :

> :H-3 : 1.125E+03 :

C-14 : 3.589E+04 :

I i

NA-24 : 1.610E+04 :

P-32 : 2.605E+06 :

]R-51 : 1.698E+04 :

N-54 : 1.576E+06 :

$kNh6 $ 123hE05 $

FE-55 : 1.110E+05 :

FE-59 : 1.269E+06 :

00-58 : 1.106E+06 :

00-60 : 7.0C7E+06 :

NI-63 : 8. 214E+05 :

NI-65 : 8.399E+04 :

CU-64 : 3.670E+04 :

ZN-65 : 9.953E+05 :

ZN-69 : 1.018E+04 :

BR-83 : 4.736E+02 :

BR-84 -: 5.476E+02 :.

Values based on Reference 1, Section 5.2.1 assunptions unless otherwise indicated in Reference 5.

3 thits - mrem /yr per nati An 1

l 00CM, Fermi-2 2.0-10 2611W/0051W,11/05/82 l

l l

l 2

l

TABLE 2.2-1 (Continued)

PATHWAY DOSE FACTORS FOR SECTION 2.2.1.b (Pg )

Page 2 of 4 i

AGE OROUP ( CHILO )

ISOTOPE : INHALATION :

__________~_________________

BR-85 : 2.531E+01 :

RB-86 : 1.983E+05 :

RB-88 : 5.624E+02 :

RB-89 : 3.452E+02 :

SR-89 : 2.157E+06 :

. :SR-90 : 1.010E+08 t

SR-91 : 1.739E+05 :

SR-92 : 2.424E+05 :

. :Y-90 : 2.679E+05 :

Y-91M : 2.812E+03 :

Y-91 : 2.627E+06 :

Y-92 : 2.390E+05 :

Y-93 : 3.885E+05 :

ZR-95 : 2.231E+06 :

ZR.97 : 3.511E+05 :

NB-95 : 6.142E+05 :

MO-99 : 1.354E+05 :

TC.99M : 4.810E+03 :

TC-101 : 5.846E+02 :

RU-103 : 6.623E+05 :

RU-105 : 9.953E+04 :

thits - mrem /yr per pCi/m3 00CM, Fermi-2 2.0-11 2611W/0051W,11/05/82 g - _ . _

m .. _ _ . _ . _ _ _ _ . _ . _ . __ . __ _ _ _ _ __ _ _ __ ..___

TABLE 2.2-1 (Continued)

PATttiAY DOSE FACTORS FOR SECTION 2.2.1.b (Pg )

Page 3 of 4 AGE GROUP ( CHILO )

ISOTOPE : INHALATION :

, :RU-106 : 1.432E+87 :

AG-110M : 5.476E+06 :

TE-125M : 4.773E+05 :

TE-127M : 1.480E+06 :

TE-127 : 5.624E+84 :

TE-129M : 1.761E+06 :

TE-129 : 2.549E+04 :

TE-131M : 3.078E+05 :

TE-131 : 2.054E+03 :

TE-132 : 3.774E+05 :

I-138 : 1.046E+06 :

I-131 : 1.624E+07 :

I-132 : 1.935E+05 :

I-133 : 3.848E+86 :

I-134 : 5.069E+04 :

I-135 : 7.918E+05 :

CS-134 : 1.014E+06 :

CS-136 : 1.709E+05 :

CS-137 : 9.065E+05 :

CS-138 : 8.399E+02 :

BA-139 : 5.772E+04 :

units - mrem /yr per pCI An3 0004, Fermi-2 2.0-12 2611W/0051W,11/05/82

TABLE 2.2-1 (Continued)

PATWAY 00SE FACTORS FOR SECTION 2.2.1.b (Py )

Page 4 of 4 AGE (ROUP ( CHILO )

ISOTOPE : INHALATION :

BA-148 : 1.743E+06 :

BA-141 : 2.919E+03 :

BA-142 : 1.643E+03 :

LA-140 : 2.257E+05 :

LA-142 : 7.585E+04 :

CE-141 : 5.439E+05 :

CE-143 : 1.273E+05 :

CE-144 : 1.195E+07 :

PR-143 : 4.329E+05 :

PR-144 : 1.565E+03 :

ND-147 : 3.282E+05 :

W-187 : 9.102E+04 :

NP-239 : 6.401E+04 : l 1

1 Units - mrem /yr per pCi/m3 I 00CM, Fermi-2 2.0-13 2611W/0051W,11/05/82

TABLE 2.2-2 PATWAY DOSE FACTORS FOR SECTION 2.2.2.b (R y )*

(For Dose Calculations Required by TS 3.11.2.3)

Page 1 of 3 AGE CROUP ( IteFANT ) ( N.A. ) ( INFANT )

,l ISOTOPE l

....................................................l INNALAT 0N l CA00N) PLANE l Get/COYen LK

. .IN-3 l 4.4seE+e2 l e.eeeE+ee l 4.eseE+e3

...................................................l

.Ic.

4 l 2.s st+e.

.......................I..e.eeeE+ee l . 9,E+e9 l ;

l :.e5st+e4 l .3e5E+er l

...................................... ............l

.INA-24 s25E+e5 -

lP.32 l 2.eaoE+es l 4.s7eE+ e l

........................i..s.eeeE+ee ..........................

.2e4E+e4

.Ics .5: l

.......................i..s.SesE+es l .5ssE+e5 l lMM-54 l 9.99st+es l 1.s25E+69 P.87sE*0s

......................................l..............l lnN.5s l 7. seE+e4 l .eseE+es e.5e7E e2

......................................l..............l lFE-55 l e.s94E+e4 l S.000E*e8 e.720E+05

......................................l..............l lrt.59 l .e:5E+es l 3.2e4E+es .se4E+es

......................................l..............l l 4.4s4E+es l 2.st:E+es

.......................................l

.Ico-5s.........I..7.77eE+e5 lco.se l 4.5eeE+es l 2.532E+ e

......................................l.. 2s9E+er l

.INi-sa l 3.3esE+e5 l eheeE+ee 2. 47E+e9

.....................................l..............l lNI-s5 5.082E+04 l 3.451E+e5 l 9.esIE-01

......................................l..............l lco-s4 l 1.49eE+64 l s.07st+e5 1.eseE*e5

......................................l..............l l2N-s5 l s.4seE+05 l .5 3E+es 8.03sE+e

......................................l..........9 l2H-s9 l 8.322E+44 l 6.e40E+ee l

1.157E-te

......................................l..............l le8-83 l 3.seeE+02 l 7.e79t+03 2.ee2

......................................l.......E-e2 .-......

l le8 64 l 4.004E+02 l 2.3s3E+85 3.7s7E-24

......................................l..............l le8-t5 2.044E+61 l l 6.eeeE+ee e.eee

......................................l.......E+ee .......

l lRI-8s l 1.904E+05 l 8.e27E+07 s.923E+e6

......................................l..............l l81-86 5.5*2E+02 l l 3.*?9E+04 5.s22

......................................l........E-es l81-89 l

l 3.20st+02 l 3.47st+05 1.024

......................................l.......E-53 l58-E9 l

l 2.e36E+6i l 2.509E+04 S.s2 2E*e9

......................................l.....

l58-90 4.446E+67 l

l l 0.000E+00 1.30

......................................l......5E+11 .......

l l58 98 l 7.334E+04 l 2.58tE+0s 8.see

......................................l.......E+05 .......

l I

i i

Values based on Reference 1, Section 5.3.1 assunptions unless otherwise indicated Reference 5.

units: Inhalation - mrem /yr per pCi An 3 Dthers -m 2

mrem /yr per pCi/sec ODCM, Fermi-2 2.0-14 2611W/0051W,11/05/82

TABLE 2.2-2 (Continued)

PATlWAY OOSE FT4CTORS FOR SECTION 2+2.2.b (Ry )

Page 2 of 3 ACE CROUP ( INFAMT ) ( M.A. ) ( INFANT >

, l IS'uf0PEl IMMALATIDH l CROUHb PLAMEl CR$eG0TeMILKl l$F-92 l 1.400E*05 l 9.638t+05 l 2.627E+0! l l lY-90 l 2.600E+05 l 5.300E+03 l 2.022E+04 l ;

.................................................... 1

- lY-98M l 2.766E*03 l 1.86tE*05 l S.620E=l?

l l l

lV-91 l 2.450E*06 l 1.207E+06 l 2.144E*05 l lY-92 l 1.266E+05 l 2.142E+05 l 3.078E-01 l lY-93 l 1.664E+05 l 2.534E+05 l 5.329E+02 l l25-95 l 1.750E+04 l 2.037E+00 l 3.458E+04 l l25-97 l 1.400E+05 l 3.445E*06 l 1.334E*03 l lHI-95 l 4.700E+05 l 1.657E+00 l 7.485E*06 l lM0-99 l 1.340E+05 l 4.626E+06 l 9.324E*06 l l[E-99M l 2.030E+03 l 2:199E+05 l 4.930E+02 l lTC-101 l 9.442E+02 l 2.260E+04 l 4 465E-58 l lFU-103 l 5.516E+0S l 1.265E+03 l 3.046E+03 l lPU-105 l 4.044E+04 l 7.212E+05 l 9.610E-02 l lPU-10i l 1.85fE*07 l 5.049E+08 l 0.l?4E*04 l lAC-IION l 3.66EE+0i l 4.019E+09 l 7.960E+06 l lTE-125M l 4.diiE+05 l 2.12SE+06 l 6.142E+46 l lTE.127M l 1.382E+0i l 1.083E+05 l 4.952E+07 l lTE-127 l 2.4 ME+04 l 3.293E+03 l 4.0?tE+03 l lTE.1261 l 1.C&OE+06 l 2.305E+07 l 4.855E+07 l lTI-129 l 2.632E+04 l 3.076E*04 l 5.035E-09 l lTE.1,ln l 1.HtE*05 l 9.459E+06 l 6.065E+05 l lTE-lit l S.216E*05 l 7.450E+07 l 4.153E-32 l l T E - 12.' l 3.40*E+0! l 4.968E+06 l 1.*54E+0i l l1-830 l 1.59dE*06 l 6.692E+06 l 2.624E+0t l thits: Inhalation - mrem /yr per pCIAri 3 Others -m 2

mrem /yr per pCi/sec l

l m)m, Fermi-2 2.0-15 2611W/0051W,11/05/82

! TABLE 2.2-2 (Cbntinued)

PATHWAY DOSE FACTORS FOR SECTION 2.2.2.b (Rg )

Page 3 of 3 ACE GROUP ( INFANT ) ( N.A. ) ( INFANT )

l ISO

.....f.0PEl INNALAtl0N l CROUND PLANE l CR$rCOT/ MILK l

+

lI 838 l 1.484E*07 l 2.009E+07 l 3.86tE+13 l lI 832 l 1.694E+05 l 1.465E*06 l 4.093E*01 l lI-833 l 3.556E+06 l 2.90tE*06 l 2.000E+09 l lI-834 l 4.452E*04 l 5.305E+05 l 2.528E-10 l lI-835 l 6.950E+05 l 2.947E+06 l 6.006E+06 l lCf-134 l 7.020E*05 l 3.007E+09 l 1.003E+11 l lCf=136 l 1.345E*05 l 1.702E+00 l 4.305E*09 l lCf-137 l 6.Il0E+05 l 1.20lE+10 l 9.235E*le l lCf-136 l 8.764E+02 l 4.802E+05 l 1.635E-22 l lPA-139 l 5.096E+04 l 1.194E*05 l 8.622E-07 l l5A-140 l 1.596E+06 l 2.346E+07 l 7.209E+06 l lDA-148 l 4.746E+03 l 4'754E+04 l 1.523E-45 l lDA-142 l 1.554E+03 l 5.064E+04 l 0.000E+00 l lLA-140 l 1.680E+05 l 2.100E+07 l 5.640E+03 l lLA-142 l 5.950E+04 l 9.122E+05 l 3.235E-07 l lCE-141 l 5.166E+05 l 1.540E+07 l 4.730E+05 l lCE-143 l 1.162E+05 l 2.627E+06 l 4.609E+04 l lCE-844 l 9.84E+06 l 9.032E+07 l 7.376E+06 l l88-143 l 4.326E+05 l 0.000E+00 l 2.370E+04 l lFF-844 l 4.264E+03 l 2.ll2E*03 l 3.513E-50 l lHI-84 3.220E+05 l 1.009E+07 l l 1.729E*04 l lw 447 l 3.*(2E*04 j 2.740E+06 l 7.504E+04 l lti8

H l 5.950E+04 l 1.976E+06 l 2 40E+03 l l Units: Inhalation - mrem /yr per pCI An 3 Others -m 2

mrem /yr per pCi/sec CDCM, Femi-2 2+ 0-16 2611W/0051W,11/05/82

2. 3 METEOROLOGICAL MODEL 2.3.1 ATHOSPERIC OISPERSION Atmospheric dispersion for releases is calculated using a mixed-mode fom of the straight line flow Gaussian model.

X/Q = average atmospheric dispersion (sec/m3) for a given wind

' direction (sector) and distance.

=2.036K{ "jk E

+ (1-E) exp (-1/2 (h/oj) )

Nr ujkIj UjkUj 2.03 = (2/n)1/2 divided by the width in radians oT a 22.50 sector (0.3927 radians).

n jk = ntsnber of hours meteorological conditions are observed to be in a given wind direction, windspeed class k, and atmospheric stability class J.

NOTE: If periodic data (hourly) are used instead of the joint frequency data, all variable subscripts are dropped, the n is set equal j,k to 1 and the hourly averaged meteorological variables are entered into the model.

N = total hours of valid meteorological data througho' u t the period of effluent release, r = distance from the release point to location of interest (meters) u jk = wind speed (midpoint of windspeed class k) measured at the 10 meter level (m/sec) during atmospheric stability class j U

jk = wind speed extrapolated to the effective release height using the wind power law with the site-specific wind power law exponent.

+ b2/2n)

(c)2 Ij = the lesser of or where 0004, Femi-2 "(303) 2.0-17 l 2611W/0051W,11/05/82 l

i oj = vertical standard deviation of the plume (meters) at distance r for releases under the stability category j indicated by AT, from Figure 2.3-1.

K = terrain recirculation factor from Table 2.3-1.

6 = plume depletion factor (radiciodines and particulates) at distance

, r for the applicable stability class. Nomally a factor of 1 is assumed or, if appropriate, may be obtained from one of Figures 2.3-2 through 2.3-5.

W = 3.1416 b = maximum height of adjacent building either upwind or downwind from the release point.

AT = vertical temperature gradient (oC/100n).

E = fraction considered ac ground level releases W

"1. 0 for _0_10 u

1 W W 2.5 8 _1.5 8 (_S. ) f or 1. 0 < _P_ S 1 .5 e.< "

W W 0.3 - 0.06 (.P_) f or 1.5 < _P_ < 5.0 u u W

0 for > 5. 0 u

W, = vertical exit velocity from the vent.

u = horizontal wind speed at the point of release.

h = effective height of release (m) b =h y +g-c 0004, Femi-2 2.0-18 2611W/0051W,11/05/82

-i N = height of release point !

= additional height due to plume rise (m):

hr for neutral or unstable conditions (AT 1 -0.5 oK/100n) w 2/3 1/3 1.44 L9.) (I.) d u d hr p . "= the lesser of or W

39d m u for stable conditions ( AT > -0.5 *C/100n):

r F 1/4 4 ( 3.)

S or F 1/3 1.5 ( *-) S-1/6

= the lesser of or

hpr for neutral or unstable conditions (in the event that r for neutral or unstable conditions 2

s is less than pr for stable conditions) d = diameter of plant vent c = correction for low vat exit velocity (m) e-W W 3(1.5 _9.) d for P.11.5 u u

=

0 for .W.9.> 1.5 u

F, = momentum flux parameter (m 4

/sec2 )

F, = (W,32 (d/2)2 ODCM, Fenni-2 2.0-19 2611W/0051W,11/05/82 '

S = restoring acceleration per unit displacement 1

8.75 x 10~4 sec-2 for -0.5 < AT < 1.5 S -

1.75 x 10-3 sec -2 for 1.5 < AT ! 4.0 2.45 x 10~3 sec -2 for AT 4. 0 2.3.2 RELATIVE DEPOSITION Relative deposition per unit area is calculated for a mixed-mode release.

D/Q = relative deposition per unit area (m-2), for a given wind direction and at a given distance.

= 2.55K r [(E) (g ) + (1 - E) Db], where D

g = relative deposition mode for the grour.d-level portion of mixed-mode releases from Figure 2.3-6.

O, = relative deposition rate for the elevated portion of mixed-mode o releases obtained from one of Figures 2.3-7 through' 2.3-9.

2.55 = [ radians per 22.50 Sector]~1 0004, Fermi-2 2.0-20 2611W/0051W,11/05/82 w v

SITE (DISTANCE- 0.8km 1.2 km 1.6km 2.4km 3.2km 4.0km 4.8km 5.6km 6.4km 7.2km 8.0km M$ BOUNDARY METERS) 0.5mi 0.75mi 1.0mi 1.5mi 2 mi 2.5mi 3.0mi 3.5m1 4.0mi 4.5mi 5.0mi OM R- N 1.13 (1249) 1.11 1.13 1.14 1.15 1.16 1.18 1.20 1.14 '

1.08 1.06 1.04 87 Q

NNE 1.32 (1646) 1.23 1.27 1.32 1.35 1.34 1.40 1.39 1.35 1.32 1.29 1.26 g" SSE 1.58 (610) 1.61 1.67 1.73 1.79 1.76 1.69 1.66 1.51 1.44 1.46 1.37 N

v. S 1.57 (1417) 1.39 1.51 1.62 1.67 1.60 1.69 1.65 1.60 1.51 1.39 1.32 sN SSW 1.14 (1542) 1.07 1.11 1.14 1.21 1.25 1,24 1.28 1.24 1.15 1.07 1.01 SW 1.43 (1920) 1.31 1.35 1.40 1.48 1. 56' ~ 1.61 1.10 1.59 1.57 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 W 1.20 (1390) 1.12 1.18 1.23 1.30 1.34 1.32 1.38 1.38 1.31 1.23 1.27 WNW 1.08 (1082) 1.05 1.09 1.12 1.16 1.16 1.20 1.26 1.30 1.26 1.14 1.08 NW 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 i i

Linear interpolation within a sector at distances lying between those shwon in the table is given by: Fp-Fg FR 32 -FR2g

-R

(R 2 1) ( 2 3j Where xR is that distance lying between the distances (R g & R2 ) specified in the table.

F &F are the values at these specified distances.

3 2 P

2 TABLE 2.3-1 Open Terrain Recirculation Factor

i

~

FIGURE 2.3-1

~

Vertical Standard Deviation of Material in a Plume (oZ )*

(Letters denote Pasquill Stability Class) I 1000 ,

l ,

/

s' I /

/ / /

. l / / , s f j f /

l l l l

/ / ,/ #

/

A

[ , / y

,A / ,

100 1 ,

s f 2"

/ / / /

B ; / / ,p -

/

/ / / / s' l l A

/ ./

C ! f -*

/ / / / '

/ ,, -

/ / / D // / /

j /// /?/ / , - /

y ! ! / p

[ 10 ' - '

/

/ /

// ,

// / J

/ / /

/ /

/, I

/

10 100 0.1 1.0 PLUME TRAVEL DISTANCE (KILOMETERS) 1 Temoerature Channe Pasquill Stability withHeicht(k)(UK/100m) Catenories Classification A Extremely unstable

<-1.9 Moderately unstable

-1.9 to -1.7 8

-1.7 to -1.5 C Slightly unstable

-1.5 to -0.5 D Neutral

-0.5 to 1.5 E Slichtly stabit

Reference 6 Moderately stable 1.5 to 4.0 F G Extremely stable

> 4.0 0004, Fermi-2 2.0-22 2611W/0051W,11/05/82 l

i

FIGLRE 2.3-2 Plune Depiction Effcet for Ground-Level Releases (All Atmospheric Stability Classes) O H

t O

l 8 :

1 1 e

/ i

. /

/ T

/ 5

=

.o

/r S

=1s i

) o

?df '5

, / EN

/

C x i.

I r

bc c1 1

/ .25 WA

, i z3

.- e WC 23 3:

o AE

1 I

I I

5 I 5I

/

E

/

~

l # h e e % y g.

o q 9'

6 6 6 a a

Reference 6 3 Wold NI DNINIYW3W NOll3VUd l

ODCM, Fermi-2 2 0-23 2611W/0051W, 11/05/82

FIGURE 2.3-3 Pltsne Depletion Effect for 30-m Relcases (Letters denote Pasquill Stability Class) o-

/ / I

, O.

i e e g e

i s /

t / / ~

///

/ / b

/// $._

W C. ( $<- 5

' .=

/

h*.

/ ._ U $

Es Em 5 #

s

/ ct 3 1 is $!! y =t I IJ g E

~ 5 I ~

11 E Il y d i // i i N // mi =

S ri 5 z ff a Q

$ E

< a N O w 3

!E8 i

-- 3 $

II %

O II II l II ?

I I

n a

o. o. e, g e, m, w, et w n

- e o e o o o e o o

Refereme 6 3 Wold NI DNINIYW5W NOll3VWd l

l l

ODCM, Fermi-2 2.0-24 l

i 2611W/0051W, 11/05/82

\

m hm w y&

. ~5. eT%Ea

, iT 8" p" ga F .5I $

,Eg.aa3%a EC gg0?* 3

! O 0 0 _

l

,I .i!

t '

= 0 E

2 _

L )0, B

m AF,\

T S (E

' ( 0 0

, g

% \ \

3 0

1

' 5

\ )

s s

a N '3 l C

L" s \ it l

l y

o RD N A) "s t

S U L l

i l

T(%NE E

N' B

)

u q

s hT A )C, S e S B, R P N E e U (A - T t t E o 0 M n e

0 O d

,% 1 L s I r K e

.q' t

( t e

E L C (

s ~ N s e

A s a

T e d, S l I e D R L n 4

E 0 V 6 A r R f o

T w% E M

U L

P t

f f

E c

e n

o 0 i t

1 l

e p .

e D _

e m

l u

P 1

0 0 ,- 8 7 s. 5 A 3 2 1 0 8 0 ,- O 0 0 0 1 0 E?28* m m2atz Ez 3Ez9y<E 8g '.3 4 Y?ti MO* 8Ex' M en i, . ) k

, m FY*

3s* F3* g ,8 s6 yXE

^a%4* E @ g0~ haEE D.E 0 0

0

- 2 0

% \ 0 5 3 0 1

g N k )

% \ u o

l C

N t y

)

s \ i b

S l

i t

e D

( t l

i L u q

A E s R ,L )

S P e

T B R U '

E t e

E A T )C, T o N S8 E e

n N 0 M A% U (A 0 1

OL d

s r

e I

t N )

0 K

(

t e

1 L E (

= C s e

G N s N A a s I N

T S

l e

e I I R

% A D

) l M L m G, E E 0 0

F, R V 1 E N A r

( l O R f o

E I T t L T E e B C e A M f A R U f

E T L S F P n

(

0 o i

1 t l

e p

' e D

e m

l u

P 1

0 0 3 7 1 0 2

0 0 8 5 A 3 2- 1 0 0 O 0 a 0 E^*3Ra m m,ag gf E z9PaE O

e

?,gr) hh

.t8wT;:

F ?m*

FIGlRE 2.3-6 Relative Deposition for Ground-Level Releases (All Atmospheric Stability Classes) ,

10 4 10-4 \

N ^ ;

lii w %.

D u 2 \

. e %m E T

\

$2 E

$ 10-5 i:

\ s N

h

. E c

\ A

$ \

Ng P

5 N %

E 10-6 s 10-7 0.1 1.0 10.0 100.0 200.0 PLUME TRAVEL DISTANCE (KILOMETERS)

Relative Deposition for Ground Level Releases (All Atmospheric Stability Classes)

Reference 6 ODO4, Fermi-2 2611W/0051W, 11/05/82 2 0-27

l FIGURE 2.3-7 Relative Deposition for 30-m Releases (Letters denote Pasquill Stability Class)

'~~

e UNSTABLE (A,B,C) i 104 ,

Q \

E [ v g / 's '

f h

{ [ \\ NEUTRAL e

/ NN 2

NEUTRAL (D) y g p 10-5 ,

k STABLE in i % ,- ", '

2 w f

' y

/Y x

\l t

O \

- ; [ s sa 5 / / x x

!= / / N g x 3 10-6 ,

M E,F,Q

\ '<

1 ;

l I

I r

l

/

10-7 0.1 1.0 10.0 100.0 200.0 PLUME TRAVEL DISTANCE (KILOMETERS)

Relative Deposition for 304n Releases (Letters denota Pasquill Stability Class)

Reference 6 ODO4, Femi-2 2.0-28 2611W/0051W,11/05/82

FIGLRE 2.3-8 Relative Deposition for 60.c Releases (Letters denote Pasquill Stability Class) 104 f , y ( UNSTABL E ( A,B,C) f X

. / N s f %y 10-5 l l f, NEUTRAL (D) k '

94w E I ;

x w

I I W

/ / N%

$ / \ % % UNSTABLE g / \ N

/

! NEUTRAL

\

3 s %

$ 104 a ;

, ~

G I

/

2 i !

E I )

5 I l P

i 5 J l E

10-7 ,

STABLE (E,F,G) 1 i

i ;

I I

.s..,

104 J l

0.1 1.0 10.0- 100.0 200.0 PLUME TRAVEL DISTANCE (KILOMETERS)

Relative Deposition for 60e Releases (Letters denote Pasquilt Stability Class)

Reference 6 0D04, Fermi-2 2.0-29 2611W/0051W,11/05/82

f FIGWE 2.3-9 Relative Deposition for 100-m Releases (Letters denote Pasquill Stability Class) 104

., _ UNSTABLE (A,B,C)

N

\ N 10-5 j p - Q I

s' %

f f NEUTR AL (D) kg '

E / / \ N

= > /

N N s.

E / / N s Ns u j s 104 , , ,

!" i i E i i E / J s' /

/ :

I I ,

5 A g STABLE (E,F,G)

NO DEPLETION i 10-7 j I

l l I I I

f

/

,- /

0.1 1.0 10.0 100.0 200.0 PLUME TRAVEL DISTANCE (KILOMETERS)

Relative Deposition for 100e Releases (Letters denote Pesquill Stability Class)

Reference 6 ODCH, Fermi-2 2.0-30 2611W/0051W,11/05/82

2.4 DEFINITIONS OF GASEOUS EFFLUENTS PARAMETERS _

Section of Tem Definition Initial Use B = administrative allocation factor for gaseous 2.1.1

. effluent pathways.

l b = maximtsn height of the adjacent building. 2 3.1 C = monitor reading of a gaseous effluent monitor corre- 2.1.1 sponding to associated saTple radionuclide concentrations.

Dg = average organ dose rate in the current year (mrem /yr) 2. 2.1. b D

p

= dose to an individual from radiciodines, tritit.sn, and radio- 2.2.2.b nuclides in particulate form with half-lives greater than eight days (mrem).

D, = average skin dose rate in current year (mrem /yr) 2.2.1.a D

t

= average total body dose rate in the current year 2.2.1.a (mrem /yr)

Dg = air dose due to betc emissions from noble gases (mrad) 2.2.2.a D = air dose due to gamma emissions from noble gases (mrad) 2.2.2.a 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.

b/Q' = 2.763 x 10 -9 m -2 in the WNW sector i

l DD04, Fermi-2 2.0-31 1 2611W/0051W,11/05/82

- - . . . . ._ _=____ _

l L

Section of Term Definition Initial Use 6 = plume depletion factor at distance r for the appro- 2.3.1 priate stability class (radiolodines and particulates).

Kg ,= total body dose factor due to gama emissions from 2.1.1 3

radionuclide (mrem / year per pCI A ) from Table 2.1-1.

l

= Skin dose factor due to beta emissions from radionuclide 2.1.1 h 3 1 (mrem /yr per pC1/m ) from Table 2.1-1 My = air dose factor due to gamma emissions from radionuclide 2.1.1 i (mrad /yr per pCi/m3 ) from Table 2.1-1.

N = air dose factor due to beta emissions from noble gas 2.2.2.a j radionuclide 1 (mrad /yr per pC1/m3 ) from Table 2.1-1.

n = number of hours meteorological conditions are 2.3.1 jk i

observed to be in a given wind direction, wind-speedclassk,andatmosphericstabilityclassJ.

N = total hours of valid meteorological data. 2.3.1 Py = dose parameter for radionuclide 1, (mrem /yr per 2.2.1.b pCI A3 ) for the inhalation pathway from Table 2.2-1.

Q = rata of release of noble gas radionuclide 1 2 1.1 3

(pC1/sec) g' = release rate of radionuclide i for the combined source 2.1. 2 terms of routine Reactor Building Exhaust Plenum plus Containment Drywell Purge Release.

Ik = cumulative release of noble gas radionuclide i over 2.2.2.a the period of interest (pC1).

CDCM, Fermi-2 . 2.0-32 2611W/0051W,11/05/82

Section of Term Definition Initial Use D'

i

= cunulative release of radiciodine, tritiun or 2.2.2.b material in particulate form over the period of interest (pC1).

g = rate of release of noble gas radionuclide 1 (pCi/sec) 2.1.3 from the Containment Drywell Purge.

Ry = dose factor for radionuclide 1, (mrem /yr per pCi/m ) 2.2.2.b 2

or (m -mrem /yr per pCi/sec). .

R = monitor reading per mrem /yr to the skin. 21.1 s

R = monitor reading per mrem /yr to the total body. 2.1.1 Dg = limiting dose rate to the total body 21.1

= 500 mrem / year.

D = limiting dose rate to the skin 2.1.1 ss

= 3000 mrem / year.

r = distance from the point of release to the location 2.3.1 of interest for dispersion calculations (meters).

g = monitor reading of the noble gas monitor at the alarm 2.1.1 setpoir,t for the release pathway under consideration.

I = vertical standard deviation of the plume with 2.3.1 j

building wake correction.

oj = vertical standard deviation of the plume (in meters), 2.3.1 at distance r for ground level releases under the stability category j indicated by AT, from Figure 2.3-2.

AT = vertical temperature gradient (*C/100n). 2.3.1 0D04, Fezmi-2 2.0-33 2611W/0051W,11/05/82

1

) Section of Term Definition Initial Use K = terrain recirculation factor. 2 3.1

= wind speed (midpoint of windspeed class k) at ground 2.3.1 ujk

. level (m/sec) during atmospheric stability class J.

s N' = relative dispersion for unrestricted areas at the 2.2.2.b controlling receptor.

X/Q = the sector-averaged relative concentration at any distance 2.3.1 3

r in a given sector. (secA )

X/Q = the highest annual average relative concentration in 2.1.1 any sector, at the site boundary. sec/m3

= 4.186 x 10-6 3,gj,3 in the NW sector X/Q i

X/Q' = relative concentration for the location occupied by 2.2.2.b the controlling receptor.

3

= 2.686 x 10-7 secA in the WNW sector U = windspeed u extrapolated to the effective release 2.3.1 jk jk height using the wind-height power law.

E = fraction of release considered as ground-level 2.3.1

< F, = momentum flux parameter (m4 sec -2) 2.3 1 h = effective release height (m) 2 3.1 ,

hy = height of release point (m) 2.3.1 0004. Feral-2 2.0-34 2611h/0051W,11/05/82

- ^ ' - '

j

't Section of Term Definition Initial Use h = additional height due to plume rise (m) 2.3.1 br W, = stack exit velocity (m sec-I) 2.3.1 S =3 restoring acceleration per unit displacement for 2.3.1 adiabatic motion in the atmosphere. (sec~ )

u = horizontal wired speed at the point of release 2.3.1 I

c ODCM, Fermi-2 2.0-35 2611W/0051W,11/05/82

- - ' - - - - - z -_ _ . . . ._ . _ . ; ; _ .. . --

1 i

2.5 GASEOUS RADWASTE EFFLUENT SYSTEM i

Figure 2.5-1 is a schematic of the Gaseous Radwaste Effluent Monitoring System showing the release points to unrestricted areas.

~

i .

Ir 1 .

]

i 4

1 ODCM, Fermi-2 2. 0-M 2611W/0051W, 11/05/82

s il i!! 1 s

i s*

r M I e* ' E s*

-}

- " T S

M

h. 5I ,' Y l

S 1 IM ,E

=

Ab s -

,,,'""s

,Y G

- 3 s

u r

e s

c M

I P

s "

" w*%

E_ N I

R M

i

'V r

j O

T I

S { .

N O

M

$ s

s

D T r r "E N

G s 's s s " E

. U L

y l , F

n. F bE

a. -

r .,.

t. I 3 8

rxm. l u.

a 4# E

. ! T j i D S

_ r A _

W D

. A y,6 -

,M Fs D

s u yTs '

2' R

S U

f f f

" _ s.

s. E O

r S 4

y 5

" _ i G

A a 3 5

0 4 u 3 3

0 4 a 3 4

0 4

. N .

N G M 1,

l 8

- N I

P I

t r, 1 l

p >

s 0 s D s D E

- ~ -

- ~ - s -

m

- ~ - l a p e t

s f u 9^

s

-g e

5 r

( c.

E 5hk n EM s Eo Tw 1 t g

C I I

V D st

&D E's

'D RL I et Dz lr o Eu ss Au Rs "su m <

t- , ' ,

' c'~

i I > l' I

~

r i

4 SECTION 3.

RADIOLOGICAL ENVIR0tNENTAL MONITORING 3.1 SAMPLING LOCATIONS Sampling locations as required in Technical Specification 3/4.12.1 are described in TabF J.0-1 and 3.0-2 and shown on the maps- in Figures 3.0-1, ,

3.0-2, and 3.0-3.

NOTE: For the purpose of implementing Technical Specification 3.12.2, sampling locations will be modified ss required to reflect the findings of the Land Use Census.

r l

l l

.(

1 l

0004, Femi-2 3.0-1 2612W/0051W,11/05/82

t 6 i

't i 1l o dhg 4

1 =als B

~

v E O d a 1 i

y 5 w w . .

_ .5. ._ . .

.\ .

..\. .

l.

s I l /. . [,. I

,r ;.. _._

l _ ., i ,. . I.

l

.g l_ii__ i

' i i I

i -

} _ l _ _1..

l'. .i ._.

a

(,

7 i

I i

j

. ';l 1 .

a g

l ,-

ti,

.)p:7e g .: I

5. ', ,9

l u .w, ix m ...: .'. a A.

._ , 1 -

E ~, i..

4 r( ' A #

i ~ - . 'f5313; L-3?tG se ELcq c i,-i

'.,y y a

? i p

a.:, ,

y, c eor.,. . c ,,

c 1

c.;:.

5

%. m . .

L. -n

, pr cr:. n, >

- I r

. ?I 'i.. h. .. , , ya . ! <k E7 .' ~ -\_; N. N4 g 1,g jj ,/

_.q/+,,; ;3 '

.<. ,e '

-.j 7-4

-Cf / , , , ,g , , ,q . . sw I

i l #. / g .: (' *[' 'sj

',..,-) g h l ' ~ '

f ,' ,l ll l

p,l ' f ~,g y ;

.,4,

' b.. [.. , \.,r4N'y% N

. s!

' i .

i i

. g( . 7t. ,.

! l .,

.,l' , t j . _

. , ). a , . -

l. N.

/l gs .

e s

..(

3 i g g t -

i

'I I*

55

r. k j '" l I '% l

!, .4 .. i !,a

['

II i 4

5 9 .. . . . - --

O -- -

- - ~

6 .

s- .

EF-2-RERP W

1o @@uCe.M 5 MP Vd%m,$ 9 Mqnw.5MaJ5 m

kl "c ve4.M w ~pl3.lMj l";.h b1 ' c.J ]Oi 3 p, w g ; ,m 3

) fQ p s QQ@ i ! il Qbf"J@!)7'o TFb ~

/ hD, M, l(

. . 1. n%n i I!- '54PFWF] T~i wi ' r{ [ {p 8

<'\f

' kk

,. ~

U is

~ Dr"

. 9 I9 d b.

C ch f 4

i ;

. .. m.,, ,s!

'* *'I,a 1- 'e, y ,

. , , I ,

,c v,, nnh.&

c 3

> g <f ;[l l n, .7.,.

7 1

,. i

+,...q . ,

on, .

-x Q.--:

i- %y MM.. LJh- l. ' Rn Q--:- ildE <

1.,.. .

ML~ L p} -

k- [!f :k b: c', hi.

,, m yc S+ sy ,. y-i OY 3;,,.. h r

m. &.

i

0 t T2 .. . g$ w A^4 kt- + %.'

m%g4MWy r! m W s...an 79 m e 1 y: r~ . w.y ,,y am 1 w , ;T n, .,1 y

~ 9pw ~&uM. e,r. q y,,=...,.=pa n

_- c_

sp ,_"re- .i x

~7 xan.a : - ag$p

- . - ~, - ,

s.a g

(

+s S

-Q ERIE

'c .

i n g s; @w pa4, v. e+g.w e gty

,,,, i

%_ m._ l

/e, n... .

, r e

g /m g.

.f

. . Q. m,i e sashv y . o*G e ,i.. ... .. -. ..n.\

ossoments O c

,' sg,

.e . . ]pi e4+h~fsee A . g.cainaissa.it. __,_, , _ ,4 s

e e s. y ~~s..,3.h-+ .

x . [, .-g~. e ;+r o mia8caat raarien.no

,_ m ...,

n: W--%

- te onr n.una ren

~ ~ ~. - a m ,,0, o u,1o. Envi e, _mosntnt u

,:p:c/ 5 4 tt q / '141 t

m, e

=tt.st s s .

$A" ,/ ==vraosar r^' =^> et=>

~ --

'\ -- -- .

ym , . . ,m "

,3. , ., , .~ ~~ . - - - - - - - - . - - - .

, s.

. 6, 9

! :: f i

+

3 s- x .a.

I -c <

g 72 e~

Z K a'* 2

e. es $ $ .)'

f. "2

.c = od a:

u a" -2. >

= dd) 4 w

" ::f=u o36 m

~

8 '

f E

g -

.-...- . . . , . - - - . . ~ . - a. . _. . s m,, .. _ J_ _ . , _ .

J I

f' -

s

\

l y z .

i, 4 e -

q

G .

iT ? -

m . -

r --

.m l

n, -

+. ,,

y

. i ;. ,,

e ,.

t, / .,

+:. .

i.

1 -

e. t- ,

4 7 l s ,,

4 !

, f 'i

. l T 4.,

n ( a 1

]m g

.s ..

i L. .

o g . :. i. a. 3r E'

, i ff' ;, '.*--

lE '

.* - s.-I,.' <

i g' -

' ~

m

L E.

' k

. s

~,.. . p' ' '

f>. /

\

y 'y i ,

.(-' ,g l ' '

.h

f. ,-

3 b \ j.

s i

m E. I B B E I 'd I i

9 6

. 2. D. . . . - -

2 -^

)

TABLE 3.O-1 ENVIRONDW!NTAL RADIOLOCICAL MONITORING FROCRAN 1982 - 1983 Nmber of Sampling Analysts Type of Sample Samples and location Device Frequency Type Frequency Remarks Direct Radiation NE - Estral Beach TWo (2) Continuous Comme dose Quarterly tocations selected by ranking NW - Site Boundary TLDs at sampling - mixed-mode annual average D/Q; NNW - Site Soundary each TLDs NE - Estral Beach serves as WNW - Site Boundary location changed closest sector as well as clos-N - Site Boundary quarterly est coesmnity with highest D/Q NNE - Residence Supplemental stations (Table NE - Community 3.0-2) 30 routine nonitoring (same as above NE - stations with two or more dost-Estral Beach) meters placed as follows: an inner ring in the general area Control - Farm of the site boundary and addt-14.5 miles W tional rings at approntaately 2, 5 & 10 miles with a station in approximately each sector of the ring, with the eyception of those sectors over take Ette.

j Fish - Vicinity of discharge Nets Sentannually - Camma Sealannually(s) Tellow perch and/or Walleye Yellow Perch or Spring and isotopic selected on basis of being a

.and/or Control - vicinity of equivalent Fall as (edible relatively abundant species that Walleye Celeron Island weather portion) is both commercial and sport in perette take Erie Shoreline 5 - Pointe Aux Peaux Crab sample Sealannually - Ca=a Semiannually (a)

Sedimente NE - Estral Beach Spring and isotopic E - Feret 2 discharge Fall as weather permits Airborne NE - Estral Beach 1. Particulate Change la. Cross Weekly (a) 1. Initiate samplir.g program on Particulates(b) . NW - Site Boundary sampler - filters oeta(b) following each gross beta and gamma too-NEl - Residence continuous weekly filter change topic, January.

SSW - Site Boundary 1 1

NE - Community 2. Radiotodine Change Ib. Comma Quarterly (a) 2. InMiste sampling program on (same as abwe NE - centster weekly tootopic composite by too.ne-131, June Estral teack) location t

Control - Fara j 14.5 miles W I

a. Samples analysed in duplicate.

b. If gross beta in air or water is greater than 10 times the mean of control semples for sny medtum, ganma isotopic performed on individual samples.

l

TABLE 3.0-1 ENVIRONMENTAL RADIOLOGICAL MONITORINC PROCRAM 1982 - 1983 (Continued)

Number of Sampling Analysis Type of Sample Samples and Incation Device Frequency Type Frequency Remarks Surface Water Fermi I potable Composite Monthly 1. Caessa Monthly (a) Composite sampler collects an water intake sampler isotopic aliquot at hourly time intervals relative to monthly compositing Control - Trenton 2. Trittim Quarterly (a) period.

Channel Power Plant composite by intake location

3. Tritium Quarterly (a) composite by location Drinking Water (b) City of Ibnroe Composite Monthly 1. Cross Monthly (a) Composite sampler collects an water intake esopler beta (b) aliquot at hourly time inter-vals relative to monthly com-Control - Detroit 2. Comma Monthly (a) positing period.

water intake at isotopic composite by Fighting Island location Cround Water Cround water Cauge Monthly 1. Measure -

Comma f ootopic & tritium quar-elevation from ground terly if ground water flow 4 wells onsite water reversal is noted and a release elevation is " suspect" from redweste.

Food Products Farms within 10 - Monthly as 1. Comma Monthly as When milk smsples not swallable miles - prefer- available isotopic available or as recessary as determined by ,i sbly those having during groir- todine during growing licensee.

the highest I/Q, ing season 131 season D/Q Milk WNW Coat - 1.6 mi. Coat, cow 1. Monthly 1. Comme Monthly 1. Initiate sampling program WSW Coat - 2.0 mi. 1sotopic on gamma isotopic - January NW Cow - 5.7 mi.

l control - Cow 2. Semi- 2. Iodine- Semi- 2. Initiate sampling program 14.5 alles W monthly 131 monthly for iodiae-131 when graz-when wt.en ing season starta, May-animals animals October oc paa- on pas-ture ture

a. Samples analyzed in duplicate. l

b. If gross beta in air.or water is greater than 10 times the mean of control samples for any medium, samma isotopic perforud on individual samples.

l TABLE 3.0-2 SUPPLEMENTARY TLD STATIONS (Continued)

Sector / Station No. Location SW S-17 Fermi gate along Point Aux Peaux Road - on fence post W of gate WSW S-18 Pole (#DEC034-35) on S corner of Toll Road S of main gate W S-19 Pole (fDE74-40H5) on Toll Road, first residence from Enrico Fermi Drive SSW S-20 Pole (fDE7785BB1) at end of Front Street - in front of Detroit Edison Generation Plant (special area)

SW S-21 Pole (#8-78-150) junction of Mortor and Laplaisance (10 mi. ring)

WSW S-22 Junction of Dixie Highway and Laplaisance/Albain (10 mi. ring)

WSW S-23 Pole (fDE4940B4) Custer (St. Mary's) Park corner of N Custer and Dixie (Monroe St.) (N side, next to river) (special area)

WSW S-24 Pole (# DECO 31-60A) Milton " Pat" Munson Recrea-tion Reserve - N Custer Road (10 mi. ring)

WNW S-25 Pole (#MTBC2) corner Stoney Creek and Finzel Roads (10 mi. ring)

NW S-26 Pole (fDECO 5028) N corner Graf ton and Ash Roads NNW S-27 Pole (fDECO 35 6 40) junction of Port Creek and Will-Carlton Roads N S-28 Pole (#064 Y-7224) SE side of I-75, corner race l and S. Huron River Drive (special area)

N S-29 Pole (fDECO 45 4 40) N side corner of Cahill and Gibralter Roads (10 mi. ring)

NNE S-30 Pole (IDE 55 40G4) S corner of Adams and Gibralter (across from Humbug Marina) (special area).

TABLE 3.0-2 SUPPLEMENTARY TLD STATIONS Sector / Station No. Location NW S-1 Pole NE Corner Dixie Highway and Post Road (2 mi. ring)

NNW S-2 Pole NW Corner Dixie Highway and Swan Creek (2 mi. ring)

N S-3 Pole (#DE5240G5) on Masserant - South on SE corner of driveway to cbandoned barn (2 mi. ring)

NNE S-4 Pointe Mouillee - W Jefferson and Campau Road, Pole (fDE7045GC3) on SE corner of bridge (5 mi.

ring)

NE S-5 Pointe Mouillee Game Area - Field Office, pole near tree north area of parking lot (5 mi. ring)

NNE S-6 Labo and Dixie Highway - Pole (#175W3909) on SW corner with light (5 mi. ring)

N S-7 Labo and Brandon - Pole (IDE6150G4) on SE corner near RR (5 mi. ring) j NNW S-8 Pole (#R56DE27305) behind post office in Newport (5 mi. ring)

WNW S-9 Pole (#R45DE40-2-30) on SE corner of War and Post Rds. (5 mi. ring)

W S-10 Pole (fMO-78SP-G7-35) on NE corner Medau and Lapard - near mobile home park (5 mi. ring)

SW S-11 Pole (IDEC03740-6) on NW corner Mentel and Hurd (5 mi. ring)

SW S-12 Pole (#DE71-4-40H) in parking lot of Department of Natural Resources Office Building - Sterling State Park (5 mi. ring)

W S-13 Pole (#DE74-5-40GC) on Williams Road - school complex approximately 200 yards S of Jefferson High (special area)

WSW S-14 Pole (#DE45-35G6R60) N side of Pearl - Woodland Beach (pop. area)

S S-15 Pole (fDE76-40H5) S side of Long and Pcint Aux Peaux (site boundcry)

SSW S-16 Pole (#DE58-40-G5RG69) S side of Point Aux Peaux -

next to vent pipe (site boundary)

ML20080E846

Text

MPC , MPC 1 1.1 MPCy g a , MPC s , MPC 7 , and MPQ

Navigation menu

Search