ML20093K266

Forwards Revised Offsite Dose Calculation Manual, Reflecting NRC Comments on Previous Rev.Specific Comments & Resolutions Listed

ML20093K266
Person / Time
Site:	Fermi
Issue date:	10/11/1984
From:	Jens W DETROIT EDISON CO.
To:	Youngblood B Office of Nuclear Reactor Regulation
References
EF2-71988, NUDOCS 8410170249
Download: ML20093K266 (2)

Text

{{#Wiki_filter:_ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ - _ _ _ _ _ _ _ _ _ _ h Wayne H. Jerts I- . Vics PresW.nt Nuclear Operstons t Ferrrw2 $40G North Dxe Highway BOMWah Newport IQUI 1 pa ssw, Mehrgart 48166 October 11, 1984 so EF2-71988 Director of Nuclear Reactor Regulation Attention: Mr.-B. J. Youngblood, Chief Licensing Branch No. 1 Division of Licensing- 'U. S. Nuclear Regulatory Commission Washington, D.C. 20555

Reference:

(1) Fermi 2 NRC Docket No. 50-341 (2) Detroit Edison letter-to NRC, " Revised Offsite Dose Calculation Manual", l EF 2-69 216, dated July 25, 1984

Subject:

Revised Offsite Dose Calculation Manual A revised Offsite Dose Calculation Manual (ODCM) is provided as the attachment to this letter. The revisions reflected l f. in the attachment and delineated-below, are a result of NRC I comments on the previous revision (Reference 2). These i p' comments were provided in a September 25, 1984 telephone conversation between C. Nichols, T. Mo, and E. Branagan of NRC and W. V. Lipton and O. K. Earle of Detroit Edison. The l NRC comments and their resolution are provided below. j a) Comment: Provide a figure in ODCM which reflects the site boundary for gaseous and liquid effluents. Resolution: Figure 4.0-1 provides the requested information. b) Comment: Provide sodrce information for the land use census used. Resolution: Section 2.2 has been modified to indicate that the initial controlling receptor location is consistent with the 1983 land use census, c) Comment: Provide a commitment to verify all computer codes used to support dose assessments described in the ODCM. 8410170249 841011 DR ADOCK 05000341 l PDR (

p: s. ?A, ~ .:'Mr. B.-J. Youngblood-i - October 11, 1984 ' EF2-71988 Page 21 ' Fermi 2 commits-to' verify th'e; 1 . Response: computer codes used to support the1 . dose assessment ~ methods discussed'in-the-ODCM. Such an evaluation,.. ' including'the development of test 1 data sets to' support; comparisons.-with ^ -external'calbulations, has'been perfor'msd on the software-Cl incorporated-to. support the effluents accountability.; system.: cc. 2 d) Comment: Confirm that the mo'nitorTtrip' setpoint for the fueljpool ventilationfexhaust monitor:is more. conservative than 10CFR20. = Resolution: Trip setpoints for: the fuel. pool ventilation exhaust: monitors will be adjucted to trip atflevels below 10CFR20 limits. Please direct'any questions to Mr. O. K. Earle~at 313-586-4211. Sincerely,- cc: Mr. P. M. Byron

• Mr. M. D. Lynch
• Mr. C. Nichols*

Mr. T. Mo* USNRC Document Control DeFk; Washington',-D.C. -20555*-

• With Attachment I'

+ k ..~.

I 0FFSITE DOSE CALCULATION MANUAL for DETROIT EDISON COWANY ENRICO FERMI ATOMIC POWER PLANT - UNIT 2 h i MAY 1984 l i 4

l 1

l CDCM, Fermi-2 2766W/0051W, 05/07/84 m1g aInAne I Y. % "_l__I Y y _0 0 j G

- TABLE CF CONTENTS List'or Tables........................... ' Li st of Fi g ures........................... iv V References...:............................ Intr GjlC ti Cr1 ; L........................ -.... vi. .l.O LIQUID E"FLUENTS.- 1.0-1 1.1 Liquid Effluent Monitor Setpoints 1.14 ' Liquid Radmaste Effluent Line Monitor... =.... _.. . 1.0-1 4 1.1.2 Circulating Water Reservoir Decant Line Monitor.... 1.0-6 1.2 Dose Calculatiop for Liquid Effluents 1.0-9 1.2.1 ~ Dose to Critical Receptor _ Due to Fish Consurption... - 1.0-9 1.2.2 Dose Due to Fish and Drinking Water Consuription.... 1.0-11 1.2.3 Methodology for Individual Liquid Case Projections... - 1.0-21 1.3 Definitions of Liquid Effluent Terms............ 1.0 1.4 Liquid Radioactivity Monitoring System........... 1.0-27 2.0 GASEOUS EFFLUENTS 2.1 Gaseous Effluent Monitor Setpoints............. 2.0-1 2.1.1 Reactor Building Exhaust Plenun, Standby Gas 2.0-1 Tieatment System, Radwaste Building Ventilation, Turbine Building Ventilation, and Onsite Storage Building Ventilation Radiation Monitors 3 2.1.2 Containment Drywell Purge............... 2.0-3 j 2.2 Gasecus Effluent Dose Rate and Dose Calculations...... 2.0-7 2.2.1 Unrestricted Area Botndary Dose Rate 2.0-7 2.2.2 Unrestricted Area Air Dose and Dose to Individual... 2.0-9 2.2.3 Methodology for Gaseous Dose Projections........ 2.0-22 2.3 Meteorological Model.................... 2.0-53 2.0-53 2.3.1 Atmospheric Dispersion 2.3.2 Relative Deposition.................. 2.0-56 i 2.4 Definitions of Gaseous Effluents Parameters 2.0-67 2.5 Gaseous Radwaste Effluent System and Ventilaticri Exhaust.. 2.0-72 Treatment System t 1 CDCM, Fermi-2 i - 2766W/0051W, 05/07/84 i i ,.,,-,._,._,,..,.m---e .,-,.....,..,-mew,y.---.,r, ,4., .-.m,,-..---,c.--.,-,--- i-,.-..c-, w

TABLE OF CONTENTS i .) c' (Continued) l Page_ -1 3.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 3.0-1 3.1 Sanpling Locations...................... 3.0-10 3.2 Interlaboratory Conparison Program............. 4.0 TOTAL DOSE FROM URANIUM FUEL CYCLE 4.1 Calculation of Total Dose fran Uraniun Fuel Cycle...... 4.0-1 d l l CDCM, Fermi-2 11 2766W/0051W, 05/07/84 l-i

LIST'0F TABLES: l Table 6.' Page-No. J i 1.0-14 1.2-1 - Bioaccumulation Factors.................. 1.0-15 1.2-2 Adult Ingestion Dose / actors'................ 1.2-3 Site Related Ingestion Oose Commitment Factor (Ag) 1.0-17 (Fish Consumption)................... 1.2-4 Slie Related Ingestion Dose Commitment Factor (A'yT) (Fish and Water Consumption).............. 1.0-19 2.1-1 Dose Factors for Exposure to a Semi-Infinite Cloud of .2.0-5 Noble Gases...................... 2.1-2 Gaseous Release Pathway Flow Rates............ 2.0-6 2.0-25 2.2-1 Inhalation Dose Factor for Infant 2.2-2 Inhalation Dose Factor for Child............. 2.0-28 2.0-31 2.2-3 Inhalation Dose Factor for Teenager 2.0-34 2.2-4 Inhaktion Dose Factor for Adults 2.0-37 2.2-5 Ingestion Oose Factor for Infant.............. 2.2-6 Ingestion Dose Factor for Child............. 2.0-40 2.0-43 2.2-7 Ingestion Dose Factor for Teenager............ 2.0-46 2.2-8 Ingestion Dose Factor for Adults............. 2.2-9 External Dose Factors for Standing on Contaminated Ground. 2.0-49 2.2-10 Individual Usage Factors................. 2.0-51 2.2-11 Stable Element Transfer Data............... 2.0-52 2.3-1 Open Terrain Recirculation Factor............. 2.0-57 3.0-1 Radiological Environmental Monitoring Program - Sample.. 3.0-2 Locations and Associated Media 1 ) 00CM, Fermi 2 111 2766W/0051W, 05/07/84 l

LIST OF FIGURES Figure No. Page No. 1.0-1 Example Calibration Curve for Liquid Effluent Monitor 1.0-8 1.4-1

Liquid Radioactivity Monitoring System.......... 1.0-28

2. 3-1. -

Vertical Standard Deviation of Material in a Plume (o ) 2.0-58 Z 2.3-2 ' Plume Depletion Effect for Ground-Level Releases..... 2.0-59 2.3-3 Plume Depletion Effect for 30-m Releases......... 2.0-60 2.3-4 Plume Depletion Effect for 60-m Releases......... 2.0-61~ 2.3-5 Plume Depletion Effect for 100-m Releases 2.0-62 2.3-6 . Relative Deposition for Ground-Level Releases 2.0-63 2.3-7 Relative Deposition for 30-m Releases 2.0-64 2.0-65 l 2.3-8 Relative Deposition for 60-m Releases 2.3-9 Relative Deposition for '100-m Releases.......... 2.0-66 ) 2.5-1 Gasecus Radwaste Effluent System............. 2.0-73 l 3.0-1 Radiological Environmental Monitoring Program 3.0-7 Sampling Locations By Station Number (Imnedate Area) 3.0-2 . Radiological Environmental Monitoring Program' 3.0, l l Sampling Locations Cy Station Number-(Greater than 5 miles) 3.0-3 Radiological Envi onmental Monitoring Program 3.0-9 Eupplementary TLD Stations By Station Number 4.0-1 Unrestricted Area Boundaries and Release Points for Liquid and Gaseous Effluents............... 4.0-2 00CM, Fermi-2 2766W/0051W, 07/23/84 iv

Refcrences 1. J. S.

Boegli, R.

R.

Bellamy, W.

L. Britz, and R. L. Waterfield, " Preparation of Radiological Effluent Technical Specifications for 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 C epliance 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 Effluents for the Purpose of Evaluating Compliance with 10CFR 50, Appendix I, U.S. EC Regulatory Guide 1.109, Rev.1 (October 1977). 4. "Envirarvnental Report, Operating License Stage", Detroit Edison Company, Fermi-2 Plant. 5. " Final Safety Analysis Report", Detroit Edison Ct.pany, Fermi-2 Plant. 6. Methods for Estimating Atmospheric Transport and Dispersion of Gaseous Effluents in Routine Releases frcrn Light-Water-Cooled Reactors, U.S. NRC Regulatory Guide 1.111 (March 1976). 7. Development of Sector-Spec!.fic Recirculation-Stegnation Factor fcr 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. 8. Methods for Estimating Atmospheric Transport and Dispersion of Gaseous Effluents in Routine Releases from Light-Water-Cooled Reactors, U.S. NRC Regulatory Guide 1.111, Rev.1 (July 1977). l COCM, Fermi-2 2766W/0051W, 05/07/84 V

INTRODUCTION The OFFSITE DOSE CALCULATION manual is a stpporting document of the RADIO-LOGICAL EFFLUENT TECHNICAL SFECIFICATIONS. As such the 00CM describes the methodolog * &nd 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 instrunentation alarm / trip setpoints. The 00CM contains a list and graphical description of the specific sample loca-tions for the radiological environmental monitoring program. Schenatic configurations of liquid and gaseous radwaste effluent systems releases to tnrestricted areas are also incitded. The 00CM will be maintained at the plant for use as a reference guide and training docunent of accepted methodologies and calculations. Changes in the calculational methods or parameters will be incorporated into the ODCM in order to assure that the 00CM represents the present methodology in all applicable areas. Computer software to perform the described calculations will be maintained current with the CDCH. l l t 00CM, Fermi-2 1810w/0051W, 05/07/84 vi

e SECTION 1. LIQUID EFFLUENTS 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 from the Circulating Water Reservoir. All releases from the Liquid Radwaste i System are to the Circulating Water Reservoir decant line. Radionuclide: concentrations are determined by analysis of samples removed from hold-up tanks after mixing to allow representativeness according to plant prccecures. 'l.1 LIQUID EFFLUENT MONITOR SETPOINTS The calculated liquid monitor setpoint values will be regarded as' upper bounds for tne 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 s liquid sample analysis data. (See Section 1.1.1). 1.1.1 LIQUID RADWASTE EFFLUENT RADIATION LINE MONITOR Dll - N007 I The liquid radwaste effluent line monitor provides alarm and automatic termination of release functio 7s prior to exceeding the concentration limits 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: 1 MPC F f ODCM, Fermi-2 1.0-1 2766W/0051W, 07/23/84

hPC a the effluent concen,tration limit (Specification 3.11.1.1) implementing 10CFR 20 for the site, corresponding to the specific mix of radionuclides in the effluent stream being considered for discharge, in y C1/ml. 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 volumetric flow of the effluent line and pro-portional to the volmetric flow of the dilution stream plus the effluent stream, represents a value which, if exceeded, would result in concentrations exceeding the limits of 10CFR 20 in the unrestri::ted area. f = the flow setpoint as detemined at the radiation monitor location, in volume per unit time, but in the same units as F, below. F = the dilution water flow setpoint as determined prior to the release point, in volme per unit time. At Femi-2, the Liquid Radwaste System Waste Sample Tanks discharge to the Circulating Water Reservoir Decant 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 detemined and set to meet the conditions of the equation for a given effluent concentration, hPC* The method by which this is accomplished is as follows: Step 1) The radionuclide concentration for a waste sample tank to be released is cbtained from the sum of measured concentrations as determined by the analyses required in STS Table 4.11-1: [ Ci=[Cg + (Ca+Cs+Cr+C) g i g where C = the concentration, C, of each measured gama emitter observed by g g gansna-ray spectroscopy of each waste sample. 0004, Fermi-2 1.0-2 2766W/0051W, 05/07/84

Cf o the concentration cf alpha emitt:rs in liquid tasta as measured in the MONTH.Y composite sample. (NOTE: Sample is analyzed for gross cm). C, = the measured concentrations of Sr-89 and Sr-90 in liquid waste as observed in the QUARTERLY composite samle. ~ C = The measured concentrations of Fe-55 in liquid waste as observed in 7 the QUARTERLY cogosite sample. C = the measured concentration of ' H-3 in liquid waste as determined t from analysis of the MONTH.Y composite sample. The C term will be included in the analysis of each batch; terms for alpha, g strontiums, iron, and tritium may be included as appropriate. Step 2) The measured radionuclide concentrations are used to calculate a l Dilution Factor, CF, which is the ratio of total dilution flow rate j to tank flow rate required to assure that the limiting concentrations ) of 10CFR 20, Appendix B, Table II, Column 2 are met at the point of discharge. DF = 1 + SF HNi + (C C y + SF C C C [ 0 a s + _f_ + t = ,g MPCg

MPC, MPC MPCr MP s

where l C = measured concentrations of C, C,, C, C and C as 1 g s f t defined in Step 1. Terms C,, C,, C, and C will be y t included in the calculation as appropriate. 4 ODO4, Fermi-2 1.0-3 2766W/0051W, 05/07/84

MPC a MPC, MPC,, MPC,, MPC, and MPC cre limiting conctntra-y g 7 t tions of the appropriate radionuclide from 10CFR 20, Appendix 8, J Table II, Colunn 2. For dissolved or entrained noble gases, the concentration shall be limited to 2 x 10 pCi/ml total activity. SF = the safety factor; a conservative factor used to compensate for statistical fluctuations and errors of measurements. (For example, [F = 0.5 corresponds to a 100 percent variation.) Step 3) The dilution flow rate setpoint for minimum dilution flow rate, F ' d is established at ninety percent of the expected dilution flow rate: (0.9) x (Circulating Water Reservoir F = d Decant Line Flow Rate ) Step 4) For the case DF < 1, the waste sample tank eff.luent concentration meets the limits of 10CFR 20 without dilution and effluent discharge flow rate may be assigned any desired value. For DF > 1, the maxim m permissible discharge flow rate, f ' must be calculated: t Fd+Ip = d for F " I ft* d P DF F where: f F = Dilution flow rate to be used in effluent monitor setpoint d calculations. F = (0.9) x (Circulating Water Reservoir Decant Line Flow Rate) d DF = Dilution Factor from step 2. f = Flow rate of Waste Sample Tank discharge. (This value will have an p upper limit of the maximun discharge capacity of the particular waste sample tank purp.) 0004, Fermi-2 1.0-4 2766W/0051W, 05/07/84 _-..,,.,-,--e.-,- ,n,--e

NOTE: If radioactivity from pirnt operations accumulatts in the Circulat-ing W;ttr Reservoir such that measurabla quantitics. of radio- = nuclides are detected in the Circulating Water Reservoir, calcula-7 . tion of F must ' include a term to account for radioactivity-d present in the dilution stream prior to the introduction of the . waste sample tank effluent: F = (Circulating Water Reservoir Decant Line Flow Rate) x (0.9) x (1 - d APE fraction of Circulating Water Reservoir). Step 5) The liquid radwaste effluent radiation monitor setpoint may now be determined based on the values of I C, ft and Fd which were 1 i specified to provide conpliance with the limits of 10CFR 20, Appendix i B, Table II, Colunn 2. The monitor response is primarily to gamma radiation, therefore, the actual setpoint is based on g C." The g monitor setpoint which corresponds to the particular setpoint concentration, c, is determined based on mcnitor calibration data or f 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.) 1 The setpoint concentration, c, is determined as follows: c = A [ C F.Ci, g g ml where A = Adjustment factor which will allow the setpoint to be established in a practical manner for convenience and to prevent spurious alarms. t (See Note 2 below) = f(actual) If A > 1, Calculate e and determine the maximun value for the actual 6aonitor setpoint (pCi/ml). ( If A < 1, No release may be made. Re-evaluate Steps 2, 3, and 4. 0004, Fermi-2 1.0-5 2766W/0051W, 05/07/84

-NOTE 1: The cciculsted. sitpoint _ concentration, c, cattblishea the bIse-R value for the moniter setpoint.. Howevgr,.in Gstablishing th2 l actual monitor setpoint for a particular monitor, background radiation levels must be -considered. Normally, the actual I monitor, setpoint includes the calculated setpoint value plus f: ~ background. Background levels - must be controlled such that radioactivity levels in the effluent stream being monitored can be accurately assessed at or below the calculated setpoint value. -NOTE 2: If DF < 1, A = (1/DF) If calculated setpoint values are near actual concentrations planned for release, it may be igractical to set the menitor alarm based on this value. In this case a new setpoint may be calculated by decreasing the effluent flow, ) increasing the dilution flow, or by decreasing { Ci by further processing cf 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 j Li@id Radwaste Effluent Radiation Monitor is determined as follows: Liquid Radwaste Effluent Radiation Monitor D11 - N007 Perform Step 2), solving the equation for DF using the appropriate values in the concentration term from the sample analyses for the Liquid Radwaste Sample Tank batch to be discharged. Then perform Steps 3), 4), and 5) to determine the monitor setpoint. If no discharge is planned for this pathway, the monitor setpoint should be Cstablished as close to background as practical to prevent spurious alarms and yet alarm should an inadvertent release occur. 1.1.2 CIRCL1.ATING WATER RESERVOIR DECANT LINE RADIATION MONITOR D11 - N402 The Circulating Water Reservoir Decant Line is the blowdown line to Lake Erie, and it furnishes dilution for liquid radwaste discharges. The radiation 0004, Fermi-2 1.0-6 2766W/0051W, 05/07/84

monitcr has no control function, but servss es support (backup) for th2 Liquid Radw:sto Effluent Lin] Monitsr. The radiation monitor setpoint is established as follows: c=([C)+ DF' g 9 I where I C and DF have values as determined in Section 1.1.1 Step 1 and 9 9 Step'*2 respectively for the liquid radwaste sample tank planned for release. (For practicality, for this monitor only, if DF is detervined to be < 1, DF may be set equal to 1 for the purpose of calculating the monitor setpoint.) 0004, Fermi-2 1.D-7 2769f/0051W, 05/07/84

FIGURE 1.0-1 EXAMPLE CALIBRATION CLRVE FOR LIQUID EFFLUENT MONITOR e C i i m L-gg. g .9 e' i s s s e, e-t.

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^1.2 DOSE CALQJLATION '~0R LIQUID EFFLUENTS For liquid dose calculations consideration is given to the two primary curr;nt of Lake. Erie. The flow patterns existing in the Lagoona Beach embayment Crximum potential individual exposure is expected to exist with the current flow in the northerly direction and only the fish consumtion 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 water consumption pathway as well as the fish consumption pathway. J The methodology for both cases is described in the following sections. 1.2.1 DOSE TO CRITICAL RECEPTOR DUE TO FISH CDNSLMPTION The dose contribution to the maximm exposed individual by way of fish consunption from all radionuclides identified in liquid effluents released to unrestricted areas is calculated using the following expression: m 4t ^1T N UR* 1 U

• 1 t

gy where D = The emulative dose commitment to the total body or any organ, T, due to radioactivity in liquid effluents for the total time period m I A tg, in mrem (Reference 1). t=1 and At = The length of the ith time period over which Cg g F are averaged for all liquid releases, in hours. g = The average concentration of radionuclide,1, in undilut'ed liquid Cg effluent during time period At from any liquid release, in g yC1/ml. = The decay constant for radionuclide 1. (sec.1) ~ l i t 1.0-9 ODCN, Fermi-2 276dW/0051W, 05/07/84 e --mva- -,----w--- .--oc ~~-w---*----m v~e--

---

e

• =%w---

-se-n- e

• e---

t -o'The -trcnsit time to the location cf. the individual expected to . g.- receiva -the gretsst potential dosa due to the liquid psthrey (1770m northeast of Fermi-2); 13,000 seconds. (Reference.5 Section .2.4.12). hWWIWd

F

= 1he near field average dilution factor for c gg g effluent release. Defined as the ratio of the undiluted liquid hte flow during release to the product of the average flow frm the discharge structure to unrestricted receiving yater times Z. \\ l ~ ) l (average undiluted liquid waste flow) Fg = laverage riow Tram the discharge structure during periods of radioactive materials release) x (Z) NOTE: The denominator is limited to 1000 cfs or less. (Reference 1, Section 4.3). where Z = Applicable dilution factor for the receiving water body at Fermi-2. Z = 10 (Reference 1, Section 4.3; Reference 5, cnapter 5, section 5.2.) A = The site related fish ingestion dose comitment factor to the total g bodf or any organ r for each identified principal gamma and beta emitter listed in Tr.ble 1.2-3 in mrem /hr per pCi/ml. Ah = K, (y BF ) DFg g where 5 K, = units conversion factor 1.14 x 10 3 10' Ci x 10 ml

• 8760 hr T

F V = Adult fish consumption (21 kg/yr). 0004, Fermi-2 1.0-10 2766W/0051W, 05/24/84

BF a Biccccunulation fccter fcr -rcdionuclide 1, in fish, in pCi/kg per g pCi/l from Table 1.2-1 (taken from Reference 3, Table A-1). 'DF = Dose conversion factor for radionuclide i, for adults in g preselected organ, t, in mrem /pC1, from Table 1.2-2 (taken from Reference 3, Table E-11). If radioact'$vity 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, F = - 1 and a t = the entire time period for which g the dose is being calculated. l 1.2.2 DOSE DUE TO FISH AND ORIfEING WATER CONSt.WTION The dose contribution to an exposed individual by way of fish and drinking ) tater consumption from all radionuclides identified in liquid effluents released to unrestricted arees is calculated using the following expression: r m -A t m At gf g A [MC e F + gg g qT [MCgge D = T gT L1 L1 j there j D = The cunulative dose comitment to the total body or any organ, T, due to radioactivity in liquid effluents for the total time period m I At, in mrem (Reference 1). g i =1 At = The length of the Ath time period over which CR and g Fg are averaged for all liquid releases, in hours. ~ C = The average concentration of radionuclide, i, in undiluted liquid g l effluent during time period At from any liquid release, in g ( yC1/ml. t 0004, Fermi-2 1.0-11 ~ 276dW/0051W, 05/07/84

r-A = The decay constant for radionuclide 1. (sec." ) g t = The transit time to the location 153On south of Fermi 2; 11,000 g s'eponds. (Reference 5 Section 2.4.12) t = The transit time to the city of Monroe - water intake; 23,000 d seconds. (Reference 5, Section 2.4.12) F The near field average dilution facter, for c during any liquid = g effluent release. Defined as the ratio of the undiluted liquid waste flow during release to the product of the average flow frun the discharge structure to unrestricted receiving water times Z. (average undiluted liquid waste flow) Fg = (average riow from the discharge structure during periods of radioactive materials release) x (Z ) NOTE: The denominator is limited to 1000 cfs or less. (Reference 1, Section 4.3). where Z = Applicable dilution factor for the receiving water body at Fernti 2. 10 (Reference 1, Section 4.3; Reference 5, Chapter 5 Section 5.2.) = 0D04, Fermi-2 1.0-12 2766W/0051W, 05/24/84

A 'gT = The site ralated drinking watcr ingestion dora consnitment factor to the total body or any organ t for each identified principal gamma and beta emitter listed in Table 1.2-4 in mrem /hr per pCi/ml. g ( w) DF A'17 =K f where = Units conversion factor 1.14 x 10' Kg t 0 3 10 Ci x 10 ml + 8760 hr T yr y 4 = Adult water consumpt?on (730 liters / year). = Dilution factor from the near field within one-quarter mile of the Dy release point to the potable water intake for adult water consunption for Fermi 2 Plant, g = 7.7 gReference 5, Chapter 5, Section 5.3) DF = Dose conversion factor for nuclide i, for adults in preselected g organ, t, in mrem /pC1, from Table 1.2-2 (taken from Reference 3, Table E-ll). A = See Section 1.2.1 h If radioactivity in the Circulating Water Reservoir Decant Line becomes > LLD, prior to the junction with the Liquid Radwaste Effluent Line, that concentration must be included in the dose determination. For this part of 1/Z, and A t = the entire time period the dose calculation, F = g for which the dose is being calculated. l 1 0D04, Fermi-2 1.0-13 2766W/0051W, 05/24/84

TABLE 1.2-1 BI0 ACCUMULATION FACTORS -(pCi/kg per pCi/11tsr)* FRESHWATER ELEMENT FISH H

9. E-01

'C 4.6E 03 NA 1.E 02 P 1.0E 05 CR 2.E 02 .. NN 4.0E 02 ~ ~* FE 1.E 02 CO 5.0E 01 NI 1.E 02 CU 5.0E 01 ZN 2.E 03 BR* 4.2E 02 RB 2.E 03 ' SR 3.0E 01 Y 2.5E 01 ZR 3.3E 00 NB 3.E 04 MO 1.0E 01 TC 1.5E 01 RU 1.0E 01 RH 1.0E 01 AG 2.3E 00 TE 4.E 02 I 1.5E 01 CS 2.E 03 BA 4.0E 00 LA 2.5E 01 CE 1.0E 00 PR 2.5E 01 l ND 2.5E 01 W 1.2E 03 NP 1.0E 01 CValues in Table 1.2-1 are taken from Refereree 3, Table A-1. 00CM, Fermi-2 1.0-14 1 2766W/0051W, 05/07/84

TABLE 1.2-2 Paga 1 of 2 ADULT INGESTION DOSE FACTORS * (mrem /pCi ingested) MUCLIGE SONE LivEt f.p0CT fava 080 E10NEY LUNC Cl-LLI t H 3 NO Data 1.35E-07 1.CS E-0 7 1.C5C-07 8.05E.07 1.05E-07 1 05E-Of C 14.. 2.84E-06 5.68E-07 5 68E-0 7 5.68E-47 5.68E-07 5.68E-07 5.68E-07 Na 24..t.70E-06 1.70E-06 1 70E-06 t.70E-06 t.70E-06 1.70E-06 1.70E-06 P 32 1.93E-04 1.20E-05

7. 4 6 E -0 6 40 Da7a NO Data NO Data 2.t?E-05 CA St NO Oafa NO Cafa 2 6*E-0 9 1.59E 0+

5 86E-to 3.53E-09 6.69E-07 NN 54 NO Oafa 4.57E-06 8.72E-Of NO Data 1.36E-06 No cafa 1 40E-05 NN 56 N0 cara 1.15E-07 2 04E-0 8 NO cafa 1.46E-07 MO Data 3.67E-06 ft SS 2.75E-06 t.90F-06 4.4 st-0 7 No cara NO Data 1.06E-06 1.09E-06

1. E 59 6.34E-06 t.02E-05 3.9 t E-0 6 40 Data NO Data 2.85E.06 3.*0E-05 CO 58 NO Data 7.45i.07 f.6 f E-0 6 NO Data No ca7a Nb cara t.5tf-05 CO 60 NO Data 2.14F-06 4.72E-06 NO DATA NO Data NO DATA 4.02E-05 NI 63 1.30E.04 9.01E-06

4. 3 6F-O o NO Cafa NO Cafa NO Defa 1 88E.06 t

NI 65 5.28E-07 6.s6E.08 3.13E-08 NO Oafa NO Data NO Data 1.74E-06 CU 66 NO Oafa 8.33E-08 3.9tE-08 NO Data 2.10E.07 Nn Data 7.80E-06 im 65 4.84E-06 1.542-05

6. 9 e E -0 6 NO Cara 3.03E-05 NO Cafa 9.70E-06 24 69 1.0 3 E -0 8 8.97E-08 1.37E-09 NO Cata t.28E-08 NO Data 2.96E-09 Sa 81 NO Data NO Cafa

4. 0 Z E -0 8 40 Data NO Data NO Data 5.79E-08 Sa 84 NO Dafa NO Data 5.2tE-08 NO Defa NO Data NO Data 4.09E-13 84 85 NO O&fa NO Cafa 2.14 E -0 9 NO Data NO Cara NO Cafa LT E-24 48 to NO Data 2.ttE-05 9.83E-06 No Data No cafa NO Data 4.16E.06 as 88 NO Data 6.0SE-08 1.2tE-08 NO Cafa NO Data NO Data 8.36E-19 48 89 NO Data 4.01E-08 2 82E-08 No cara No cafa No cafa

2. 3 3 E 54 89 3.08E-04 NO cafa 8.86E-06 NO Cara NO Cafa NO Data 4.94E-05 la 90 7.58E-03 40 Data 3.86E-03 No Cafa No cafa NO Data 2.19E-04 la 91 5.67E-06 NO Data

2. 21E.0 7 No Data NC Data NO Data 2.70E-05 Sa 92 2.15E-06 NO Defa 9.30E-08 No cafa NC caTA NO Data 4.2 6E-05 Y 90 9.62E-09 40 Data 2.58E.10 NO Data No cafa NO 06fa 1 02E-04 1

9tm 9.09E-11 No cafa 3.52E-12 NO Cafa NO Oafa No cafa 2.67E-to Y 91 1 4 t E.0.7 No Data

3. ? ? E-0 9 NO Data NO Data No cara 7.76E-05 7

92 8.45E*to NO Cafa 2.NTE.11 NO Cara NO Data No Data 1.48E-05 -..............e-- Y 93 2.68Et01 NO Data 7.40E-It NO Oafa NO Data N0 cafa 8.50E-0$* 24 95 3.04E-08 9.75E-09 6.60E-09 NO Data t.53E.08 No Data 3.09E-05 ga 97 1.68E-09 1.39E-10 1.55E-10 No cafa 5.12E-to NO Data 1.05E-06 N4 95 6.22E-09 3.46E-09

1. 8 6 E -0 9 NO Data 3.42E-09 NO Data 2.10E-05 NO 99 NO Data 4.3tf-06 8.20E-0 F t0 Data 9.76E-06 NO Cafa 9.99E.0.

TC 99a 2.47E-10 6.98!-80 8.89E-09 NO cafa 1.06E-08 3.42E-10 4.13E-07 TClot 2.54E-to 3.66E-to

3. 5 9 E -0 9 NO Data 6.59C-09 1.87E-to I.10E-21 tut 03 1.85E-07 NO Data

7. 9 f f -0 8

=0 Data 7.06E-07 NO CaTA 2.16E-05 aut03 1.54E.08 No Cara 6.08E-09 No cafa 1.99E-07 No Oafa 9.42E-ca CValues in Table 1.2-2 are taken from Reference 3, Table E-11. 1 1.0-15 0004, Fermi-2 2766W/0051W, 05/07/84 I l I I t I

TABLE 1.2-2 (Continued) - Paga'2 of 2 f

=vCt:0E scNE ttvEn r.s00v rN,notC sto=Er tu=c st-tti aut06 2.r5E.06 %0 cara

3. 4 e E -0 7 No Cara 5.itE.06 No Cara t.7st-06 acitoa. t.60E-07 t.4st.or e.79E-Os 50 Data 2.9tE-07 No cara 6.04E-05 ret 25a 2 6st-06 9.7tt.07 3 5sE-07 e.06E.07 1.09E.05 NO Data

t. ort-05 FEt27=

6.77E.06 2.42C-06 a. 25E -0 7 8.73E-06 2.75E-05 NO cara 2.2FE-05 TE127 1.10E-OF 3.95E-00 2.3eE-Os 3.tSE-08 4.4eE.07 NO Cara e.6et-06 FEt29a 1.tSE-05 4.29E-06 3.a2E-06 3.95E-06 4.80E-05 40 Cata 5.79E-05 I IEt29 3.t4E-Os 1.let.08 7.6sE.09 2.6tE-08 1.32E-07 No cara 2.37E.08 TEl3tn-1.73E-06 s.661-07 7.05E-01 8.34E-06 s.57E-06 NO Cara e.60E-05 FEt31 8.97E-Os-e.23E 09

6. 2 2 E -09 1 62E.08 S.63E-05 No cara 2.79E............................................................................

18132 2.52E-04 1.63E-06 1.5AE.06 1 00E-06 1.57E-42 NO Cara f.71E-05 t 130' 7.56E-07 2.2 3E.06 s.40E-07 1.e9E-06 3.6eE-06 No Cafa 1.92E-06 t 131 6.16E-06 5.95E-06 3.4tE-06 1 95E-03 1.02E-05 NO Cara 1.57E-06 l i 132 2 03E-07 5.63E-07 3 90E-07 t.90E-05 a.65E-07 No cara 1.02E-07 I 133 1 62E.06 2.4FE-06 7.53E-07 3 63E-04 6.3tE-06 No caTA 2.22E-06 8 136 1.06E-07 2.seE-07 1.03E-0F 4.99E-06 6.5eE-07 No cara 2.5tt-10 t 135 6.63E-v7 t.16E-06 4.23E-07 7.65E-05 los6E-06 No cara 1.3tt-06 C5 36 6.22E-05 1.4eE-06 1.21E-06 NO Cata 6.79E-05. l.59E-05 2.59E-06 C5336 6.5tE-06 2.57E-05 1.85E-05 NO Cata 1 63E-05 1 96E-06 2.92E-06 C5137 7.97E-05 1.09E-06 7.14 E -0 5 90 Data 3.70E-05 1 23E-05 2.tlE-06 C5138 5.52E-08 1.c9E-07 5.60E-Os NO Cata 8.01E-04 7.9tE-09 6.65E-13 sal 39 9.70E-os 6.9tE-Il

2. 8 4 E -0 9 'NO caTa 6.46E-tt 3.92E-11 1.72E-07 3a160 2.03C-05 2.551-00 1.33E-06 wo nata s.*Ft.09 t.66E-Os 6.tet.05 P.at*1 6.FIE-Os 1.56E-Il 1.59E-09 NO Cata 3.3tE-It 2.02E-fl 2.22E-17 9al*2 2.13E-00 2.19E-tt 1.3*E-09 NO Cafa t.35E-It 1.26E-it 1.00E-26 Lat*C 2.30E-09 1.262 09 J.3JC-10 40 Data No Data 40 Data 9.25E-05 tat *2 1.2eE-10 5.82!-11 1.65E-It NO Data NO Data 40 Cara 4.25E-07 CEt44

9. *J 6 E -0 9 6.33E-09

7. t eE-10 NO cafa 2.94E-09 NO DATA 2.62E.05 CEl*3 8.65E-09 1.22E-06 1.35E-t o NO Data

5. 3 7 E.10 NO CaTa 6.56E-05 CEt**

6. nee-07 2.96E-07 2.62E-Os NO Cafa 1.2tE-07 NO Cafa 1 65E-06 pat *3 9.20E-09 3.69E-09 4 56E-to NO Data 2.13E-09 NO Cafa 6.c3E-05 pat **

-3.otE-Il I.23E-Il 8.5 sE-12 NO Data 7.05E-t2 NO Cara 6.33E-te 40167 6.29E-09 7.2fE-09

6. 3 5 E-10 NO Ca f a 6.25E-09 NO Data

,3 69E-05 4 197 1.03E-07 8.6tE-04 3.01 E-o s No cata NO Data 40 Data 2.e2E-05 i 87239 1 19E-09 1.17C-10

6. 4 5 E.1 1 40 Data 3.65E.10 40 cara 2 40E.c5 l

CValues in Table 1.2-2 are taken from Reference 3, Table E-11. l 0004, Fermi-2 1.016 2766W/0051W, 05/07/84 ~

TABLE 1.2-3 Page 1 of 2 SITE RELATED INESTION DOSE COMMITMENT FACTOR, Ah (FISH CONSLNPTION) (mram/hr per pCi/ml) NUCLIDE - BONE LIVER T.30DY THYROID KIDNEY LUNG GI-LL1 H-3 0.00E+00 2.26E-01 2.26E-01 2.26E-01 2.26E-01 2.26E-01 2.26E-01 C-14 3.13E+04 6.2CE+03 6,26E+03 6.26E+03 6.26E+03 6.26E+03 6.26E+00 Ha-24 4.07E+02 4.0?E+02 4.07E+02 4.0?E+02 4.07E+02 4.07E+02 4.07E**2 F-32 4.62E+0? 2.S?E+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 4.3SE+03 S.35E+02 0.00E+00 1.30E+03 0.00E+00 1.34E+0c Mn-56 0.00E+00 1.10E+02 1.95E+01 0.00E+00 1.40E+02 0.00E+00 3.51E+00 Fe-55 6.5SE+0 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+00 Co-56 0.00E+00 8.92E+01 2.00E+0 0.00E+00 0.00E+00 0.00E+00 1.81E+00 Co-60 0.00E+00 2.56E+02 5.65E+02 0.00E+00 0.00E+00 0.00E+00 4.81E+00 Hi-63 3.11E+04 2.16E+03 1.04E+03 0.00E+00 0.00E+00 0.00E+00 4.50E+02 Fi-65 1.26E+02 1.64E+01 7.49E+00 0.00E+00 0.00E+00 0.00E+00 4.17E+02 Cu-64 0.00E+00 9.97E+00 4.6SE+00 0.00E+00 2.51E+01 0.00E+00 8.50E+02 2n-65 2.32E+04 7.37E+04 3.33E+04 0.00E+00 4.93E+04 0.00E+00 4.64E+0c 2n-69 4.93E+01 9.43E+01 6.56E+00 0.00E+00 6.13E+01 0.00E+00 1.42E+01 Fr-83 0.00E+00 0.00E+00 4.04E+01 0.00E+00 0.00E+00 0.00E+00 5.82E+01 Ir-84 0.00E+00 0.00E+00 5.24E+01 0.00E+00 0.00E+00 0.00E+00 4.11E-Oc Ir-S5 0.00E+00 0.00E+00 2.15E+00 0.00E+00 0.00E+00 0.00E+00 1.01E-15 Fb-86 0.00E+00 1.01E+05 4.71E+04 0.00E+00 0.00E+00 0.00E+00 1.99E+0c Fb-SS 0,00E+00 2.90E+02 1.54E+02 0.00E+00 0.00E+00 0.00E+00 4.00E-09 Fb-69 0.00E+00 1.92E+02 1.35E+02 0.00E+00 0.00E+00 0.00E+00 1.1 E-13 fr-89 2.21E+04 0.00E+00 6.35E+02 0.00E+00 0.00E+00 0.00E+00 3.55E+00 Sr-90 5.44E+05 0.00E+00 1.34E+05 0.00E+00 0.00E+00 0.00E+00 1.57E+0c fr-?1 4.07E+02 0.00E+00 1.64E+01 0.00E+00 0.00E+00 0.00E+00 1.94E+00 Sr-92 1.54E+02 0.00E+00 6.68E+00 0.00E+00 0.00E+00 0.00E+00 3.06E+02 Y-90 5.76E-01 0.00E+00 1.54E-02 0.00E+00 0.00E+00 0.00E+00 6.10E+00 Y-91m 5.44E-03 0.00E+00 2.11E-04 0.00E+00 0.00E+00 0.00E+00 1.60E-02 i-91 S.44E+00 0.00E+00 2.26E-01 0.00E+00 0.00E+00 0.00E+00 4.64E+00 Y-92 5.0iE-02 0.00E+00 1.4SE-03 0.00E+00 0.00E+00 0.00E+00 8.66E+02 i 4-93 1.60E-01 0.00E+00 4.43E-03 0.00E+00 0.00E+00 0.00E+00 5.09E+00 - r-95 2.40E-01 7.70E-02 5.21E-02 0.00E+00 1.21E-01 0.00E+00 2.44E+02 - r-97 1.33E-02 2.68E-03 1.22E-03 0.00E+00 4.04E-03 0.00E+00 C.30E+02 l'b-95 4.47E+02 2.4BE+02 1.34E+02 0.00E+00 2.46E+02 0.00E+00 1.51E+06 t:o-99 0.00E+00 1.03E+02 1.96E+01 0.00E+00 2.34E+02 0.00E+00 2.39E+02 Tc-9?m 6.87E-03 2.51E-02 3.19E-01 0.00E+00 3.01E-01 1.23E-02 1.48E+(' ic-101 9.12E-03 1.31E-00 1.29E-01 0.00E+00 2.37E-01 6.7"E-03 3.95E-lo Fu-103 4.43E+00 0.00E+00 1.91E+00 0.00E+00 1.692+0! 0.00E+00 5.17E+02 Fu-105 3.69E-01 0.00E+00 1.46E-01 0.00E+00 4.76E+00 0.00E+00 2.26E+0'{ l i i ODCM, Fermi-2 REY.0 1.0-17 l 2766W/0051W, 01/31/83 i

TABLE 1.2-3 (Continu;d) P ge 2 of 2 a NUCL1DE SONE liver T. BODY THYROID KIDNEY LUNG GI-LLI Ru-106 6.50E+01 0.00E+00 0.33E+00 0.00E+00 1.27E+02 0.00E+00 4.26E+03 Rg-110m 8.01E-01 8.15E-01 4.64E-01 0.00E+00 1.60E+00 0.00E+0's 3.33E+02 Te-125m 2.57E+03 9.30E+02 3.44E+02 7.72E+02 1.04E+04 0.00E+00 1.02E+0c Te-127m 6.48E+03 0.32E+03 7.90E+02 1.66E+03 2.63E+04 0.00E+00 2.17 E + 0.- Te-127 1.05E+02 3.78E+01 2.28E+01 7.80E+01 4.29E+02 0.00E+00 9.31E*03 Te-129m 1: 10E+04 4.11E+03 1.74E+03 3.78E+03 4.60E+04 0.00E+00 5.54E+0c Te-129 3.01E+01 1.13E+01 7.33E+00 2.31E+01 1.26E+02 0.00E+00 2.27E+0! Te-131m 1.66E+03 0.10E+02 6.75E+02 1.28E+03 0.21E+03 0.00E+00 8.04E+0c Te-131 1.89E+01 7.08E+00 5.96E+00 1.55E+01 8.26E+01 0.00E+00 2.67E+00 Te-132 2.41E+03 1.56E+03 1.47E+03 1.72E+03 1.50E+04 0.00E+00 7.30E+0c I-130 2.71E+01 8.01E+01 3.16E+01 6.19E+03 1.25E+02 0.00E+00 6.89E+0! 1-131 1.49E+02 2.14E+02 1.22E+02 7.00E+04 3.66E+02 0.00E+00 5.64E+01 1-132 7.29E+00 1.95E+01 6.82E+00 6.82E+02 3.11E+01 0.00E+00 3.66E+00 1-133 5.10E+01 8.87E+01 2.70E+01 1.30E+04 1.55E+02 0.00E+00 7.9?E+0! I-134 3.81E+00 1.03E+01 3.70E+00 1.79E+02 1.64E+01 4.00E+00 9.01E-03 I-135 1.59E+01 4.17E+01 1.54E+01 2.75E+03 6.68E+01 0.00E+00 4.70E+01 Cs-134 2.9BE+05 7.09E+05 5.79E+05 0.00E+00 2.29E+05 7.61E+04 1.24E+0c Cs-136 3.12E+04 1.23E+05 S.86E+04 0.00E+00 6.85E+04 9.38E+03 1.40E+0c Cs-137 3.82E+05 5.22E+05 3.42E+05 0.00E+00 1.77E+05 5.89E+04 1.01E+0c (s-135 2.64E+02 5.22E+02 2.59E+02 0.00E+00 3.84E+02 3.79E+01 2.23E-03 i En-139 9.29E-01 6.62E-04 2.72E-02 0.00E+00 6.19E-04 3.75E-04 1.65E+00 Ia-140 1.94E+02 2.44E-01 1.27E+01 0.00E+00 8.30E-02 1.40E-01 4.00E+02 Ia-141 4.51E-01 3.41E-04 1.52E-02 0.00E+00 3.17E-04 1.93E-04 2.13E-10 Ba-142 2.04E-01 2.10E-04 1.2SE-02 0.00E+00 1.77E-04 1.19E-04 2.87E-19 La-140 1.50E-01 7.54E-02 1.99E-02 0.00E+00 0.00E+00 0.00E+00 5.54E+03 i La-142 7.66E-03 3.48E-03.6.68E-04 0.00E+00 0.00E+00 0.00E+00 2.54E+01 1 Co-141 2.24E-02

1. 5 2 E-0 2-1.72E-03 0.00E+00 7.04E-03 0.00E+00 5.79E+01 Ce-143 3.95E-03 2.92E+00 3.23E-04 0.00E+00 1.29E-03 0.00E+00 1.09E+02 Ce-144 1.17E+00 4.88E-01 6.27E-02 0.00E+00 2.90E-01 0.00E+00 3.95E+02 l

Fr-143 5.51E-01 2.21E-01 2.73E-02 0.00E+00 1.27E-01 0.00E+00 2.41E+03 Fr-144 1.80E-03 7.49E-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-81 0.00E+00

2. C' ) E + 0 :-

W-187 2.96E+02 2.47E+02 8.65E+01 0.00E+00 0.00E+00 0.00E+00 8.10E+0c im-2?9 2.55E-02 2.80E-03 1.54E-03 0.00E+00 8.74E-03 0. 00E +00 _5. 75 E + 0;__ 1 i i 4 1 00CM, Fermi-2 REV.0 1.0-18 j 2766W/0051W, 01/31/83 I . _ _ _ _ _ _ _ _ ~,. _ _ _ _, _ _ _,, _... _ _ _ _ _ _ _.... _,. _.. _ _ _ _ _.. _ _ _, _ _. -.. _ _ _ _ _ _.,.,

TABLE 1.2-4 Page ). of 2 SITE RELATED INGESTION DOSE COMMITMENT FACTOR, A' l -(WATER CONSLMPTION) (mrem /hr.per pCiAnl) ~ NUCLIDE BONE LIVER T. BODY '1HYROID KIDNEY IRL ' GI-LLI H-3 0.00E+00 1.14E+00 1.14E+00 1.14E+00 1.14E+00 1.14E+00 1.14E+00 C-14 3.06E+01 6.14E+00 6.14E+00 6.14E+00 6.14E+00 6.14E+00 6.14E+00 Na-24 1.83E+01 1.83E+01 1.83E+01 1.83E+01 1.83E+01 1.83E+01 1.83E+01 P-32 2.09Ev03 1.30E+02 8.06E+01 0.00E+00 0.00E+00 0.00E+00 2.35E+02 Cr-51 0.000+00 0.00E+00 2.87E-02 1.71E-02 6.34E-03 3.82E-02 7.23E+00 Mn-54 0.00E+00 4.94Et01 9.43E+00 0.00E+00 1.47E+01 0.00E+00 1.52E+02 Mn-56 0.00Et00 1.24E+00 2.21E-01 0.00E+00 1.58Ev00 0.00E 00 3.96E+01 Fe-55 2.97Et01 2.05E+01 4.79E+00 0.00E+00 0.00E+00 1.15Et01 1.18E+01 Fe-59 4.69E+01 1.10E+02 4.22E+01 0.00E+00 0.00E+00 3.08Ef01 3.68Et02 Co-58 0.00E+00 8.05E+00 1.81E+01-0.00E+00 0.00E+00 0.00E+00 1.64E+02 Co 0.00Et00 2.31E+01 5.10E+01 0.0qg+00 -0.00E+00 0.00E+00 4.35E+02 Ni-63 1.40E+03 9.74E,41 4.71E+01 0.00E-00 0.00E+00 0.00E+00 2.03E+01 Ni-65 5.70E+00 7.42E-01 3.38E-01 0.00E+00 0.00E+00 0.00E+00 1.88E+01 Cu-64 0.00Et00 9.00E-01 4.22E-01 0.00E+00 2.27E+00 0.00E+00 7.68Ejg T Zn-65 5.23E+01 1.66Ev02 7.52E+01 0.00E+00 1.11E+02 0.00E 00 1.05E+02 Zn-69 1.11E-01 2.13E-01 1.48E-02 0.00E+00 1.39E-01 0.00E+00 3.19E-Q2 Br-83 0.00Et00 0.00E+00 4.35E-01 0.00E+00 0.00E+00 0.00E+00 6.26E-01 Br-84 -0.00E+00 0.00E+00 5.64E-01 0.00E+00 0.00E 00 0.00E+00 4.42E-06 Br-85 0.00E+00 0.00E+00 2.31E-02 0.00E+00 0.00E+00 0.00E+00 1.08E-17 t Rb-86 0.00E+00 2.29E+02 1.06E+02 0.00E+00 0.00E+00 0.00E+00 4.49E+01 Rb-88 0.00E+00 6.53E-01 3.47E-01 0.00E+00 0.00E+00 0.00E+00 9.04E-12 Rb-89 0.00E+00 4.34E-01 3.05E-01 0.00EIDO 0.00E40 0.00E+00 2.52E-14 Sr-89 3.32E+03 0.00E+00 9.56E+01-0.00E+00 0.00E+00 0.00E+00 5.34E+02 1 Sr-90 8.19E+04 0.00E+00 2.01E+04 0.00E+00 0.00Et00 0.00E+00 2.36E+03 Sr-91 6.13E+01 0.00E+00 2.48E+00 0.00E+00 0.00E+00 0.00E+00 2.92E+02 Sr-92 2.32E+03 0.00E+00 1.01E+00 0.00E+00 0.00E+00 0.00Et00 4.61E+02 4 l Y-90 1.04E-01 0.00Et00 2.79E-03 0m00ETOO 0.00E+00 0.00E+00 1.10E+03 Y-91Jn 9.82E-04 0.00E+00 3.81E-05 0.00E+00 0.00E+00 'O.00E+00 2.88E-03 Y-91 1.52E+00 0.00E+00 4.08E-02 0.00E+00 0.00E+00 0.00E+00 8.39E-e02 Y-92 9.13E-03 0.00E+00 2.68E-04 0.00E+00 0.00E+00 0.00E+00 1.60E+02 Y-93 2.90E-02 0.00E+00 8.00E-04 0.00E+00 0.00E+00 0.00E,00 9.18E+02 I Er-95 3.29E-01 1.05E-01 7.13E-02 0.00Ev00 1.65E-01 0.00Et00 3.34Ev02 l Zr 1.82E-02 3.66E-03 1.68E-03 0.00E+00 5.53E-03 0.00E+00 1.14E+03 (- Nb-95 6.73E-02 3.74E-02 2.01E-02 0.00Et00 3.70E-02 0.00E+00 2.27E+02 Mc>-99 0.00E+00 4.66E+01 8.86E+00 0.00E+00 1.05E+02 0.00E+00 1.08E+02 l 'It-99 2.68E-03 7.55E-03 9.61E-02 0.00E+00 1.15E-01 3.70E-03 4.47E+00 l 'It-101 2.74E-03 3.96E-03 3.88E-02 0.00E+00 7.12E-02 2.03E-03 1.19E-14 0004, Fermi-2 REV.0 1.0-19 2766W/0051W, 01/31/83

TABLE 1.2-4 (Continued) Page 2 of 2 " NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG G'f-LLI Ru-103 2.00E+00 0.00E+00 8.61E-01 0.00E+00 7.64E+00 0.00E+00 2.34E+02 Ru-105 1.66E-01 0.00E+00 6.57E-02 0.00E+00 2.16E+00 0.00E+00 1.02E+02 Ru-106 2.97E+01 0.00E+00 3.77E+00 0.00E+00 5.74E+01 0.00E+00 1.92E+03 Ag-110m 1.73E+00 1.60E+00 9.51E-01 0.00E+00 3 14E+00 0.00E+00 6.53E+02 Ta-125m 2.90E+00 1.05E+01 3.88E+00 8.71E+00 1.18E+02 0.00E+00 1.16E+02 TI-127m 7.31E+01 2.61E+01 8.92E+00 1.87E+01 2.97E+02 0.00E+00 2.45E+02 Ta-127 1.19E+00 4.27E-01 2.57E-01 8.81E-01 4.84E+00 0.00E+00 9.38E+01 _Ta-129m 1.24E+02 4.64E+01 1.96E+01 4.27E+01 5 18E+02 0.00E+00 6.26E+02 'Ta-129 3.39E-01 1.28E-01 8.27E-02 2.61F-01 1.43E+00 0.00E+00 ?.56E-0J Ta-131m 1.87E+01 9.14E+09 7.62E+00 1.45E+01 9 26E+01 0.00E+00 9.0SE+02 Ta-131 2.13E-01 8.90E-02 6.73E-01 1.75E-01 9 32E-01 0.00E+00 3.01E-02 Ta-132 2.73E+01 1.77E+01 1.65E+01 1.95E+01 1.70E+02 0.00E+00 5.34E+02 I-130 8.17E+00 2.42E+01 9.51E+00 2.04E+03 3 77E+01 0.00E+00 2.0dE+01 I-131 4.49E+01 6.43E+01 3.69E+01 2.10E+04 1.10E+02 0.00F+00 1.70E+01 I-132 2.19E+00 5.87E+00 2.05E+00 2.05E+02 9 35E+00 0.00E+00 1.10E+00 I-133 1.53E+01 2.68E+01 8.14E+00 3.92E+03 4.66E+01 , 0.00E+00 2.40E+01 I-134 1.15E+00 3 12E+00 1.llE+00 5.39E+01 4.95E+00 0.00E+00 2.71E-03 I-135 4.79E+00 1.25E+01 4.62E+00 8.27E+02 2.01E+01 ' O 00E+00 1.42E+01: 1.31E+03 0.00E+00 5.18E+02 i 1.71E+02 2.61E+01 Cs-134 6.73E+02 1.60E+03~ 2.00E+02 0.00E+00 1.55E+02 i 2.12E+01 3 16E+01 Cs-136 7.04E+01

2. IGE +32 Cs-137 8.61E+02 1.18E+03 7.71E+02 0.00E+00 4.00E+02 l.32E+02 2.29E+01 Cs-138 5.96E-01 1.18E+00 5.83E-01 0.00E+00 8.66E-01 8.55E-02 5.03E-06 Be-139 1.05E+00 7. 47 E-0 '6 3.06E-02 0.00E+00 6.99E-04 4.23E-04 1.86E+00

~Ba-140 2.19E+02 2.75E-01 1.44E+01 0.00E+00 9.38E-02 1.58E-01 4.52E+02 Ba-141 5.09E-01 3.84E-04 1.71E-02 0.00E+00 3.57E-04 2.18E-04 2.40E-10 Ba-142 2.30E-01 2 36E-04 1.45E-02 0.00E+00 2.00E-04 1.34E-04 3.25E-19 La-140 2.70E-02 1 36E-02 3.60E-03 0.00E+00 0.00E+00 0.00E+00 1.00E+03 La-142 1.39E-03 6.29E-04 1.57E-04 0.00E+00 0.00E+00 0.00E+00 4.60E+00 Ce-141 1.01E-01 6.84E-02 7.77E-03 0.00E+00 3 18E-02 0.00E+00 2.61E+02 Ce-143 1.78E-02 1 32E+01 1.45E-03 0.00E+00 5.81E-03 0.00E+00 4.92E+02 Ce-144 5.27E+00 2.21E+00 2.83E-01 0.00E+00 1.31E+00 0.00E+00 1.78E+03 Pr-143 9.95E+02 3.99E-02 4.92E-03 0.00E+00 2.30E-02 0.00E+00 4.35E+02 Pr-144 3.25E-04 1.35E-04 1.65 E-05 0.00E+00 7.62E-05 .0.00E+00 4.68E-ll Nd-147 6.79E-02 7.86E-02 4.70E-03 0.00E+00 4.60E-02 0.00E+00 3.77E+02 W-187 1.11E+00 9.31E-01 3 25E-01 0.00E+00 0.00E+00 0.00E+00 3 05E+02 Np-239 1.29E-02 1.26E-03 6.97E-04 0.00E+00 3 95E-03 0.00E+00 12.60E+02 l I 00CM, Fermi-2 REV.0 1 0-20 2766W/0051W, 01/31/83

METHODOLOGY FOR INDIVIDUAL LIQUID DOSE PROICTIONS (To Determine Necessity of Operating Liquid Radwasta Treatment System 1.2.3 Th2 NRC requires that dose projections be performed to indicate whether cumu-lative doses over a thirty-one (31) day period are likely to exceed 25% of the (31) day period. . cnnual design objective dose limit adjusted to a thirty-one The.25% actuation levels of 0.06 mrem total body dose and 0.2 mrem organ do i for operation of g 0:;re selected by NRC based on their cost-benefit analys s When the thirty-one (31) day projected dose exceeds 0.06 radwaste systems. operation of appropriate nrem to the tctal body or 0.2 mrem to any organ, J portions of the radwaste systems would be required. When the percent of the quarterly limits exceed 4% for the total body or any organ (i.e. the cumulative total body dose exceeds OAS mrem and the cum organ dose exceeds 0.2 mrem) determine the thirty-one (31) day dose pro es follows: tb(accumulated) x 3I 0 ~~ tb(prj) X o(accumulated) x [3f = X D (prj) L o there for the elapsed = the cumulative total body dose Otb(accumulated) portion of the current quarter plus the release under consideration for the particular reactor unit. = the cumulative organ doses for the elapsed portion D (accumulated) of the current quarter plus the release under o l consideration for the particular reactor unit. = the number of days into the current quarter to the X nearest whole day. 1.0-21 00CN, Fermi-2 2766W/0051W, 05/24/84

If activiti;s pltnned during the remhinder Gf the 31-day period ara expect d to contributo a significant doso and the det;rminati n can b2 reasonably made, this contribution should be included in the equations: ~ ~ tb(accumulated) x 3/ + Danticipated D X tb(prj) D (accumulated) x [3d o + D X anticipated D (prj) o .there = the anticipated total body or organ dose resulting Danticipated from anticipated operational occurrences which may occur in addition to routine releases over the r thirty-one (31) day period. > 0.2 mrem, 0.06 mrem or if D (prj) If Dtb(prj) o the appropriate portions of the Liquid Radwaste Treatment System must be used to process liquid waste prior to release. 1.0-22 0D04, Fermi-2 2766W/0051W, 05/24/84 -w-. -ww -9 w.-o w

• w+w-p-ew- *

.er-.-- , + -y

1.3 DEFIt4ITIONS OF LIQJID EFFLUENT TERMS Section of Initial Use T:rm Definition 1.1.1 adjustment factor applied to facilitate setting actual A = monitor setpoints. 1.2 the site related ingestion dose commitment factor due A, = y to fish consumption to the total body or any organ T for each identified principal gamma and beta emitter listed in Table 1.2-3 in mrem-ml per br-yCi. 1.2.2 the site related ingestion dose connitment factor due to A'g = water consumption to the total bo'.iy or any organ t for each identified principal gamma and beta emitter listed in Table 1.2-4 in mrem /hr per pCi/ml. 1.2.1 - Bioaccumulation Factor for nuclide i, in fish, pCi/Kg per BF = f pCi/1, from Table 1.2-1. 1.1.1 the effluent concentration limit (Specification 3.11.1.1) hPC = implementing 10CFR 20 for the site, in pCi/ml. 1.1.1 the effluent concentration of alpha emitting nuclides C, = observed by gross alpha analysis of the MONTH Y composite sample. 1.1.1 The concentration of Fe-55 in liquid wastes as C = 7 observed in the QUARTERLY composite sample. 1.1.1 the effluent concentration of a gamma emitting nuclide, g, C = g observed by gamma-ray spectroscopy of the waste sample. l 1 1.1.1 the concentration of nuclide i as determined by the C = g analysis of the waste sample. 1.0-23 l 0004, Fermi-2 l 2766W/0051W, 05/24/84 l l l

S;ction of T^rm Definition Initial Usa C = th(, a(crage concentration of radionuclide, i, in undiluted 1.2.1 g from any liquid liquid effluent during time period Atg release, in yCi/ml. the concentration of Sr-89 or Sr-90 in liquid wastes 1.1.1 C, = 'a's determined by analysis of the QUARTERLY composite sample. the measured concentration of H-3 in liquid waste 1.1.1 C = t as determined by analysis of the MONTH Y 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. DF = a dose conversion factor for nuclide, i, for adults in 1.2.1 y preselected organ,t, in mrem /pCi found in Table 1.2-2. D = the cumulative dose commitment to the total body or any 1.2.1 l organ,T, from the liquid effluents for the total time period. DF = the dilution factor, which is the ratio of the total 1.1.1 i dilution flow rate to the effluent stream flow rate (s) required to assure that the limiting concentration of ) 10CFR, Part 20, Appendix B, Table II, Column 2 are met at the point of discharge. F = the dilution water flow monitor setpoint as determined 1.1.1 prior to the release point, in volume per unit time. (General expression for equation on page 1.0-1.) t F = the, flow rate of the dilution stream used for setpoint 1.1.1 d calculations during the time of release, which is (0.9) x actual dilution flow. 0004, Fermi-2 1.0-24 g 2766W/0051W, 05/24/84 4

Section cf T rm Definition Initial Use f = effluent flow rate 1.1.1 p f = the flow setpoint as determined for the radiation monitor 1.1.1 location. (General expression.) f = maximum permissible affluent flow rate 1.1.1 g during any 1.2.1 F = the near field average dilution factor for Ch g liquid effluent release. K = 1.14 x 10', units conversion factor. 1.2.1 g 1*1'1' MPC = E, E,, E,, E,aM Et" f g g the limiting concentrations of the appropriate gama emitting radionuclides, alpha emitting radionuclides, strontium, iron and tritium, respectively, from 10CFR, Part 20, Appendix B, Table II, Column 2. SF = the safety factor, a conservative factor used to compen-1.1.1 sate for statistical fluctuations and errors of measure-l 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) 1 00CM, Fermi-2 1.0-25 27&SW/005]W, 05/07/84 i 1 ~.... _, _ _ _ _ _. _ _. _ _ _ _ _. _ - - _. _. _. - - - - _ _. -

Section cf Term Definition Initial Use t, '= The transit time to the location of the individual 1.2.1 expected to receive the greatest potential dose due to the liquid pathway; 13,000 seconds. (Reference 5 .Section 2.4.12) t = The transit time to the location 153On south of Fermi 2; g 11,000 seconds. (Reference 5, Section 2.4.12) at = duration of release under consideration. 1.2.1 o = number of liquid releases. 1.2.1 U = 21 kg/yr, fish consurption (adult). 1.2.1 F l j y = adult water consurption, 7301/ year. 1.2.2

1. 2.1-2 a Applicable dilution factor for the receiving water body at Fermi 2j 10 i

, = The decay constant for radionuclide i. (sec~1) 1 1.2.1 1 1 1 0004, Fermi-2 1.0-26 276dW/0051W, 05/07/84 h ---,n-,,- -n-- ,-nve~,- - -.-,,-- -e,--,r,, - ~

'1.4 LIQUID RADI0 ACTIVITY MONITORING SYSTEM FIQJRE 1.4-1 is a Schematic of the Liquid Radioactivity Monitoring System -showing the release points to the unrestricted area. I 1 i t 0004, Fermi-2 1.0-27 i 2766W/0051W, 05/07/84 f ^ ,- - - - - -, ~ or, ,.,- -+.-. - - - - --m-

FIC1RE 1.4-1 Liquid R dioactivity Honitoring System /Vm h[ h as s 1@ ~g l8E! EV 3 NW 8 2 se a a <~ ~ 05 D5 O2 u, C IE( " 'J,f*d g %f a 5 5 m L_ ii )!( ) g -p i !s g W ~ EEj 5 lI! rTT l li n; j c ir.3 r lid f [

g h,

-iW b ( )sI 9-e 11 11 !O~ 1 e r$ [5 G E -]o E n,n l N.a d L ni n:, d k~hkE s i b'- 1 n w s-

$m3s (a

s m 5 B I .U g is -$9 4 h -$O !l lU ~ cr ( EE o e } wir ~ c st -d"'; z ,i s n,h La 1 = i 0004, Fermi-2 1.0-28 2768t/0051W, 05/07/84 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 correnponds 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 l be established as close to background as practical to prevent spurious alarms yet alarm should an *riadvertent release occur. If a calculated setpoint is less than the monitor reading associated with the particular release pathway, no release may be made under current conditions. i Under such circumstances, the number of simultaneous release pathways may be reduced or contributing source terms may be reduced and the setpoint recal-culated. 4 2.1.1 REACTOR BUILDING EXHAUST PLENLN, STANDBY GAS TREATMENT SYSTEM, RADWASTE l BUILDING VENTILATION, SERVICE BUILDING VENTILATION, TURBINE BUILDING VENTILATION, AiO ONSITE STORAGE BUILDING VENTIALATION EXHAUST RADIATION 4 MONITORS t Monitors: D 11 - N407; D 11 - N406A ar.d B; D 11 - N403; l D 11 - N405; D 11 - N404; and Dil-N508 For the purpose of implementation of Technical Specification 3.3.7.12, the alarm setpoint level for these noble gas monitors will be calculated as follows: 2 C = aonitor reading of the noble gas monitor at the alarm setpoint 3 concentration. l (B x SF) x Rt x %B = the lesser of 4 or l C3 (B x SF) x R xD 3 as ODCM, Fermi-2 2.0-1 2673W/0051W, 05/24/84 I i .,.-. _ _.~,_ ~,~.

SF o s',fsty factcr; o consIrvativ2 factor applicd to each noble g:s monitor to compensate for. statistical. fluctuations and crrors of (. For example, SF = 0.5 corresponds to a 100 percent measurement. variation.) B = an administrative allocation factor applied.to apportion the release setpoints among all gaseous release discharge ~ pathways to .41sure 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 allocaticn factors for all simultaneous release pathways does not exceed 1. (For ease of implementation, 8 may be set equal to 1/n, where n is the number of simultaneous final gaseous release points.) kB = Dose rate limit to the total body of an individual which is 500 mrem / year. R = monitor reading per mrem /yr to the total body t =C+ X/Q [(Ki Q) Rt i i C = monitor reading of a noble gas monitor corresponding to the grab 4 sample radionuclide concentrations taken in accordance with RETS Table 4.11.2.1.2-1. For batch releases the sample must be taken prior to release; for continuous releases the sample is taken during the release. The monitor response corresponding to the measured concentration is determined from the monitor calibration curve for the particular monitor. 775 = the highest annual average relative concentration at the site boundary. (If desired, ' the annual average relative concentration at the site boundary for the particular release point may be used.) = 4.186 x 10 'sec/m in the NW sector. ~ l l 00CM, Fermi-2

2. 0-2 2673W/0051W, 05/24/84

K o totcl body dose frctor due to gamm3 emissions from radionuclide i g '(cr~em/yr par pCi/m ) from Ttblo 2.1-1. ~ g = rate of relear noble gas radionuclide i' (pC1/sec) from the release pathway under considerations the product of X and gy F, wMre X is the concentration of radionuclide i for the ) y yy (X, [ particular release volume and F is the release ficwrate. 1 y in pCi/cc and F in cc/sec.) e y p i NOTE For all radiation monitor setpoint determinations assume a fixed flow rate which corresponds to the maximum flow rate for a particular release pathway. The applicable flow rate values for use in determining radiation monitor j setpoints are found in Table 2.1-2. [ I D = Dose rate limit to the skin of the body of an individual in an l ss unrestricted area which is 3000 mrem / year. R = conitor reading per mrem /yr to the skin s C + M[ILi + 1.1 M ) Qi R = 1 s i-L = skin dose factor due to beta emissions from radionuclide 1 (mrem /yr y 3 per pC1/m ) from Table 2.1-1. 1.1 = mrem skin dose per mrad air dose i M = air dose factor due to gama emissions from radionuclide 1 (mrad /yr y 3 per pCi/m ) from Table 2.1-1. 0004, Fermi-2 2.0-3 2673W/0051W, 05/24/84

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

• Oi+91 and where q1 =

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

i TABLE 2.1-1 i i DOSE FACTORS FOR EXPOSURE TO A SEMI-IW INITE CLOUD OF NOBLE GASES * .Nuclide ~ y-Body'" (K) 8-Skin ***(L) y-Air **(M) 8_-Air"(N ) Krkl5m 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 1.6E+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 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-335 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

• • mrad-m3 p01-yr

'" mrem-m3 l pC1-yr 3 '"' 1.17E+03 = 1.17 x 10 ODCN, Fertni-2 2.0-5 2673W/0051W, 05/24/84

TABLE 2.1-2 GASEOUS RELEASE PATHWAY FLOW RATES Release Pathway Flow Rate (cc/sec)*

1. '

Reacto,r Building Exhaust Plenum 5.1E+7 (011-N407) 1.06 2. Standby Gas Treatment System (011-N406A and B) 1.4E+7 3. Radwaste Building Ventilation (011-N403) 4. Service Building Ventilation 1.07 (011-N405)

1. 8E+ 8 5.

Turbine Building Ventilation (011-N404) 6. Onsite Storage Building Ventilation

2. L 6 (011-N508) 1 i

• Reference 5 l

t 0004, Fermi-2 2.06 2673W/0051W, 05/24/84 i =_

7-2e2 GASEOUS EFFLUENT DOSE HATE AND DOSE CALCULATIONS Initial controlling receptor selection is consistent with the 1983 land use census. 2.2.1 UNRESTRICTED AREA BOUNDARY DOSE RATES 2.2.1.a Dose Rates Due To Noble Gases For the purpose of implementation of STS 3.11.2.1.a. the dose rate at the unrestricted area boundary due to noble gases shall be calculated as follows: D = t tal body dose rate at time of release (mrem / year) t X/Q (K Q) = g g D a skin dose rate at time of release (mrem /yr) s X/Q[ (L + 1.1 M )Q = g g g 1 (NOTE: terms defined previously in Section 2.1.1) In the event of simultaneous releases, dose rates shall be sumed to assure that dose rate limits are not exceeded.

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 calculat-ed for the purpose of implementation of Technical Specification 3.11.2.1.b as follows:

O = organ dose rate at time of release (mrem /yr) g X/Q (P Q') = yg 00CM, Fermi-2 2.0-7 2673W/0051W, 07/23/84 t

where X/Q = the highest annual average relative concentration in any sector at the site boundary. (The highest annual average or the annual average determined for the particular release point may be used.) = 4 186 x 10~' sec/m3 in the NW sector (highest annual average) l P =' organ dose parameter for organ o and radionuclide 1, (mrem /yr per gg 3 pCi/m ) for inhalation determined as follows: P = K (BR) T g0 yg and where 6 K constant of unit conversion,10 Ci/p Ci = BR = breathing rate for child age group 3 3700 m / year (Table 2.2-10) (from Reference 3) = DFg = inhalation pathway dose factor for child age group for organ o and radionuclide i (Table 2.2-2) (from Reference 3) Qf = release rate of non-noble gas radionuclide 1 (required by Technical Specification 3.11.2.1.b)(p Ci/sec) for the type of release under consideration. NOTE: In order to assure that potential dose rates (pre-release) to an organ due to radiciodine, tritium and particulates in simultane-ous gaseous releases from the site do not exceed 1500 mrem / year as specified in Technical Specification 3.ll.2.l(b), potential organ dose rate D must be limited as follows: o Do+ (B x SF) < 1500 mrem / year I ODCH, Femi-2 2.0-8 2673W/0051W, 05/24/84 l

there B cnd SF cre cssigned the same values C, w^re used in Section 2.1 for the release source pathway under consideration. To further ensure that-dose rate limits were not exceeded, (post-release) dose rates from simultaneous releases shall be summed. 2.2.2 UtRESTRICTED AREA AIR DOSE AND DOSE TO INDIVIDUAL 2.2.2.a Alt. 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 detennined as follows: D = air dose due to gamma emissions from noble gas radionuclide 1 (mrad) Y -8 [- ~~ 3.17 x 10 gpg(X/Q) ( = where -8 3.17 x 10 = the fraction of one year per one second = cumulative release of noble gas radionuclide i over the period of interest (p C1) for the type of release under consideration. M = defined in Section 2.1.1 y I X/Q = 4.186 x 10-6 sec/m3 in the NW sector (This is the highest annual average; the annual average for the particular release point l may be used if desired). D = air dose due to beta emissions from noble gas radionuclide 1 (mrad). g l l i = 3.17 x 10-8 {. Ng (X/Q) ( N = air dose factor due to beta emissions from noble gas radionuclide 1 g 3 (mrad /yr per pC1/m from Table 2.1-1). l ODCM, Fermi-2 2.0-9 2673W/0051W, 05/24/84

2.2.2.b Dose To An Individual In Unrestricted Area Dose to an individual from radiciodines, tritim, and radioactive materials in particulate form will be calculated for the purpose of implementation of Technical Specifications 3.11.2.3 and 3.11.2.4 as follows:

D). = dose to an organ of an individual from radiciodines, tritium, and radionuclides in particulate fom (mrem). 3.17 x 10-8 W' (R,gp) Q = where -8 3.17 x 10 = fraction of one year per one second. W' = pathway-dependent relative dispersion for p unrestricted areas at the controlling sector. r 77Q' = annual average relative dispersion parameter for location of controlling critical receptor. X/Q' applies to inhalation and all tritium pathways only. (For all tritium pathways, the D ' source term is limited to tritim.) i = 2.686 x 10' ' sec/m' in the WW section for inhalation and all triti m pathways. W'= p IITQ' = annual average deposition parameter for location of controlling (critical) receptor. D/Q' applies to all other pathways. l f = 2.763 x IU ' m in WW sector for all other -8 L pathways. 0004, Fermi-2 2.0-10 l 2673W/0051W, 05/24/84 1

mw, (NOTE: One or both dispersion values (X4' and/or UM') may be required sin the determination of organ doses to an individual depending upon the organ dose pathway present and applicable to the critical receptor.) h'- = cumulative release of radionuclide 1 (requimd by Technical Specifi-cation 3.11.2.3) over the period of interest (pC1). (For tritium pathways, the h' source term is limited to tritium.) R = pathway-specific, individual age-specific, organ. dose factor for radionuclide i, ~ pathway p, organ j, and individual age group, a. The controlling individual age group and the dose pathways are determined through the Land Use Census for the site. R,gp) is detemined as follows: (NOTE: At Fermi-2 Plant the controlling ' receptor is an infant. The dose pathways are inhalation, ground-plane, 'and grass-goatwnilk). Inhalation Pathway Factor 3 R,gp) K'(BR), (DFA )), mrem /yr per pC1/m = g where 0 K' = constant of unit conversion 10 pCi/pCi (BR), = the breathing rate for a particular age group in m / year from l Table 2.2-10. (infant = 1400) l (DFA = the inhalation dose factor for receptor age group a and for radionuclide 1, in mram/pci from Tables 2.2.-1 through 2.2-4. (Infant, Table 2.2-1) i l l 0D04, Femi-2 2.0-11 2673W/0051W, 05/24/84

Ground-Plane Pathway Factor Raipj K'K" ($$ (OFG j) ((1-e )/A1) (m2 mrom/ year per pCi/sec) i = K' = constant of unit conversion,10 pCi/pci. K" ' = constant of unit conversion, 8760 hr/yr. SF' = shielding factor, 0.7 (dimensionless) DF( = ground plane dose conversian factor for radionuclide 1 (same for 2 all age groups) (mrem /hr per pCi/m ) Table 2.2-9. A = decay constant for radionuclide 1. 1 8 t = exposure time, 4.73 x 10 sec (15 years). Grass-Goat-Milk Pathway Factor ~A t f f, + (1-f f,)e lh e"A tlf K, S(U,p) F,(r)(OFi )), i p p R,gp) = g y t l (m mram/yr per yCi/sec) I i j where (NOTE: Fermi-2 Plant Site-Specific values are included in parentheses follow-ing each definition.) K' = a constant of unit conversion,10' pC1/pci. 1 = the goat's consumption rate, in kg/ day (wet weight). (6) U,, = the receptor's milk consumption rate for age group a, in liters /yr from Table 2.2-10. 4 (infant - 330) r DD(N, Fermi-2 2.0-12 267)W/0051W, 05/24/84 ., _... _ _ _. _ _ -... -.. ~. _ _ _. - -.., _ _, - -

\\ 't -s a the agricultural productivity by unit cred*if pasture fccd grass, in Y P 2 kg/m. (0.7)- J - w s s 2 Y = the agricultural productivit.ysby unit area of stored feed, in kg/m, s (2.0) i ,-'s Cs l F, .= The; stable element transfer ccefficients, in days / liter. \\ (see Tadle 2.2-11.). ~, = fraction of deposited activity retained on feed grass. .A, r (1.0 for radiciodines; 0.2 for particulates). ' ~' \\ (OF ), = the organ ingestion dose factar for the ith radionuclide for the receptor in age group a, in mrem /pCi from Tables 2.2-5 k through 2.2-E. w s (intant - Tatle 2.2 5) 6, t -{\\ .] A ~ g = the decay constant for the ith radionuclide, in sec ls s A, = the decay constant for removal of activity on leaf and plant sur-faces by weathering, 5.73 x 10-7 -1 (corresponding to a.,14 h sec day half-life). r, 't = the transport time from pasture to goeti to milk, to receptor, in 7 sec. i 5 (1.73 x 10 ) s t.,, = the transport time from pasture, to harvest, to goat, to milk, (td o_.', Neeptor, in sec. (7.,78 x 10 ) i \\ ' 4 N, e f,I = fraction of, the yea that the goat is on pasture (dinensionless). -P ,/ (.5) I f, = fraction of,the goat feed that is pasture grass while the goat is on pasture (dimensionless). (.5) y I ?x m I 4 06CN, Femi-2 2.0-1F 267M/0051W, 05/24/84 i ,l 3, h I y \\ I ls v { ?* Ik [

Fcr tritium.in railk, the grass-goat-milk pathway fcctst is a special casa due to the fcct that the concentraticn Cf tritium in milk is bastd on airborn3 - concentration rather than deposition: 3 = K'K'" F,Q u,p(DFL )), [0.75(0.5/H)] (mrem /yr per pCi/m ) R,gp) p g where: 3 Km. = a constant of unit conversion,10 gm/kg. 3 H = absolute humidity of the atmosphere, in gm/m. (8) 0.75 = the fraction of total feed that is water. 0.5 = the ratio of the specific activity of the feed grass water to the atmospheric water. and other parameters and values are given above. 2.2.2.c Dose Calculations To Support Other Specific Technical Specifications Fo'r the purpose of implementing STS 6.9.1.9 dose calculations will be per-formed using the above equations with the substitution of average meteorologi-cal parameters for the period of the report, and the appropriate pathway receptor dose factors (R, ). (Values for R,gp) are determined in accordance with Section 2.2.2.d.) For the purpose of implementing STS 6.9.1.11, dose calculations may be per-formed using the above equations with the substitution of the dispersion para-meters (X/Q, D/Q) which are concurrent with actual releases, and the appropri-l ate pathway receptor dose factors (R,1pj). (Values for. R,fp) are deter-mined in accordance with Section 2.2.2.d). 'ODO4, Fermi-2 2.0-14 2673W/0051W, 05/24/84 .,e----,---,--wr 4 w-, ---~<-%-..y --.-,-.,..v- -,,,,-,..*-..w.---a.-wv-e,or,r. -,w-,,.,,-u-,- ~,--w-c-

Fcr the purpose cf implementing STS 3.12.2, dos 2 calculations may be per-formed using the cbove cquations substituting th2 cppropriate pathray rectptor dosa factors (ggpj) and the appropriate dispersion parameters for the loca-tion (s) of interest. Annual average dispersion parameters (6 month average for D/Q) may be used for these calculations. (Values for R,gpj are deter-mined in accordance with Section 2.2.2.d). 2.2'.2.d Additional Pathway Dose Factors For the purpose of implementing STS 6.9.1.9, 6.9.1.11 or 3.12.2, it may be necessary to calculate individual doses due to gaseous releases via exoosure pathways other than ground plane, inhalation, and grass-goat-cilk pathways presented in Section 2.2.2.b. Methodology for calculating doses due to gaseous releases via the grass-cow-milk, grass-cow-eeat and the vegetation pathwa[is the same as was presented in Section 2.2.2.b. However, R,yp) is pathway-dependent and is calculated for the remaining pathways as follows: Grass-Cow-Milk Pathway Factor R,gp) K, yg(U,p) F,MQ)), p s + (1-I I )e'A t ff ln ,-A t3f ps = y y i, w s (m mrem /yr per pCi/sec) where (NOTE: Parameter values given in parentheses are to be used in lieu of site-. Mcific values. (Reference 3.)) K' = a constant of unit conversion,10 pCi/pC1. g = the cow's consumption rate, in kg/ day Twet weight). l (50) U,p = the receptor's milk consumption rate for age group a, in liters /yr from Table 2.2-10. l l l ' NOTE: These pathways do not presently exist. Methodology is presented for use in the event that subsequent land use census results indicate such a requirement. ODCM, Fermi-2 2.0-15 2673W/0051W, 05/24/84

Y a the cgricultural productivity by unit crco of pasture fced gress, in 2 kg/m, (0.7) 2 Y, = the agricultural productivity by unit area of stored feed, in kg/m, (2.0) 1 F, ' = The stable element transfer coefficients, in days / liter. (see Table 2.2-11.) r = fraction of deposited activity retained on feed grass. (1.0 for radiciodines; 0.2 for particulates) (DF ), = the organ ingestion dose factor for the ith radionuclide for the receptor in age group a, in mrem /pCi from Tables 2.2-5 through 2.2-8. = the decay constant for the ith radionuclide, in sec~1 A y A, = the decay constant for removal of activity on leaf and plant 10-7 ~1 sec (corresponding' to a surfaces by weathering, 5.73 x 14 day half-life), t = the transport time from pasture to cow, to milk, to receptor, in g sec. 5 (1.73 x 10 ) t = the transport time from pasture, to harvest, to cow, to milk, to h 6 receptor, in sec. (7.78 x 10 ) f = fraction of the year that the cow is on pasture (dimensionless). p (0.5) f, = fraction of the cow feed that is pasture grass while the cow is on pasture (dimensionless). (0.5) t ODO4, Fermi-2 2.0-16 2673W/0051W, 05/24/84 6 w w-- --,-,-----,ea ,e. .--,e -e--. +---e-r r --m., m,*m-, w-w<< mw-n

~ Fcr.trkkkun in Gilk,. the grass-cow milk pathwry fcet r is a special case due t3 the fcct that' the concentration of tritium in milk is bas;d en airborna concentration rather than deposition:- R,gp) = K'K"'F,Qg,p(OFLg), [0.75(0.5/H)] (mrem /yr per pCi/m ) where: 4 K'", = a, constant of unit conversica,10 gm/kg. H =. absolute humidity of the atmosphere, in gm/m. (8) 0.75 = the fraction of total feed that is water. 0.5 = the ratio of the specific activity of the feed grass water to the atmospheric water. and otner parameters and values are given above. Grass-Cow-Meat Pathway Factor p s (1-f f )e-A 4.(U,P) F (rM lh -A t ff ps e if gj ), = 0 R,y ) y Y, y ,A 7 p 2 (m mrem /yr per pCi/sec) where (NOTE: Parameter values given in parentheses are to be used in lieu of site-specific values. (Reference 3)) 0 K' = a constant of unit conversion,10 pCi/pCi. I = the cow's consumption rate, in kg/ day (wet weight). (50) l l 00CM, Fermi-2 2.0-17 2673W/0051W, 05/24/84 i

U.p o the riceptor's meat consumption rato for cge group a, in kg/yr from Table 2.2-10. Y = the agricultural productivity by unit area of pasture feed grass, in p .kg/m. (0.7). Y, = the agricultural productivity by unit area of' stored feed, in kg/m. (2.0) F- = The stable element transfer coefficients, in days /kg. 7 (see Table 2.2-11.) r = fraction of deposited activity retained on feed grass. (1.0 for radiciodines; 0.2 for particulates) (DF ), = the organ ingestion dose factor for the ith radionuclide for the receptor in age group a, in mrem /pCi from Tables 2.2-5 through 2.2-8. ~ ll = the decay constant for the ith radionuclide, in sec y A, = the decay constant for removal of activity on leaf and plant sur-faces by weathering, 5.73 x 10~7 -1 sec (corresponding to a 14 day half-life). t = the transport time from pasture to cow, to meat, to receptor, in g sec. 6 (1.73 x 10 ) t = the transport time from pasture, to harvest, to cow, to meat, to h 6 receptor, in sec. (7.78 x 10 ) i f = fraction of the year that the cow is on pasture (dimensionless). P (0.5) 0D04, Fenni-2 2.0-18 2673W/0051W, 05/24/84 9

f, a frcction of the cow feed that is pastura grcss thil2 the con is on pasture-(dimensionless). (0.5) For tritium in meat, the grass <:ow-< neat pathway factor is a special case due to the fact that the concentration of tritium in meat is based on airborne concentration rather than deposition: 3 R,gp3 = K'K'"F Q g,p(DFLg), [0.75(0.5/H)] (mrem /yr per pCi/m ) f where: 4 K'" = a constant of unit conversion,10 gm/kg. H = absolute htrnidity of the atmosphere, in gm/m. (8) O.75 = the fraction of total feed that is water. 0.5 = the ratio of the specific activity of the feed grass water to the atmospheric water. and other parameters and values are given above. Vegetation Pathway Factor a 4t At~ R,gp) K' y zz,A,) M )), ,,, f e $ A + U,3 g f = fe g g y where (NOTE: Parameter values given in parentheses are to be used in lieu of site-specific values. (Reference 3)) 0 K' = a constant of unit conversion,10 pCi/pC1. 3 OD01, Fermi-2 2.0-19 2693W/0051W, 05/24/84 l

U a the consmption rat'J Cf fr;sh lcafy VIgetetion by the recrptor in g age group a, in kg/ year. (See Table 2.2-10)) U = the consumption rate of stored vegetation by the receptor in age group a, in kg/ year. (See Table 2.2-10)) f = ttw fraction of the annual intake of fresh leafy vegetation grown g locally. (1.0) f = the fraction of the annual intake of stored vegetation grown locally. g ( 0.76) t = the average time between harvest of leafy vegetation and its conssp-g tion in seconds. 4 (8.6 x 10 ) t = the average time between harvest of stored vegetation and its consmp-h tion in seconds. 6 (5.18 x 10 ) Y = the vegetation areal density, in kg/m. (2.0) y (DF ), = the organ ingestion dose factor for the ith radionuclide for the receptor in age group (a), in mrem /pCi from Tables 2.2-5 through 2.2-8. = the decay constant for the ith radionuclide, in sec~1 A g i A = the decay constant for removal of activity on leaf and plant sur- -1 (corresponding to a 14 faces by weathering, 5.73 x 10-7 sec day half-life). I i l ODN, Fermi-2 2.0-20 l 2673W/0051W, 05/24/84 l l '~

Fdr tritium in v:getation,'the-vegetation pathray fcctor is a speciel' case due to the' fact that the concentration'of tritium in vegetation is based on air-borne. concentration rather than deposition: lR g g + U,3 g) (OFL )), [0.75(0.5/H)] (mrem /yr per yC1/m ) K'K".(U f: f = dpj g J where: 3 K'". = a constant of unit conversion,10 gm/kg. H = absolute hmidity of the atmosphere, in gm/m. (8) 0.75 = the fraction of total vegetation that is water. 0.5 = the ratio of the specific activity of the vegetation water to the atmospheric water. and other parameters and values are given above. i l l I l ODCM, Femi-2 2.0-21 2673W/0051W, 05/24/84 -y. + -,,w, wr ..,,w,_..- -ww-,-- .,w =w

2.2.3 METHODOLOGY FOR GASEOUS. DOSE PRO ICTIONS i (To Determine Necessity of Operating Gastous Radwaste Trcatment System) ~ f The M C requires that dose projections be performed to indicate whether cumu-lative doses.over a thirty-one (31) day period are likely to exceed 25% of the. f annual design objective dose limit adjusted to a thirty-one (31) day period. The.25% actuation levels of 0.3 mrem to any organ, 0.2 mrad gamma air dose, and 0.4 m,r,ad, beta air dose were selected by t'e EC based' on their When the thirty-one cost-benefit' analysis for operation of radwaste systems. (31) day projected dose exceeds 0.3 mrem to any organ, 0.2 mrad gamma air dose or 0.4 mrad beta air dose, operation of appropriate portions of the radwaste systems would be required. When the percent of the quarterly limit exceeds 4% for any organ, gamma air dose or beta air dose (i.e., the cumulative organ dose exceeds 0.3 mrem, the cumulative gama air dose exceeds 0.2 mrad or the cumulative beta air dose exceeds 0.4 mrad) determine the thirty-one (31) day dose projection as follows: ~ Dy air (accumulated) Xbyy] O yair(prj) f X S air (accumulated) 31 Sair(prj) X tb(acetsnulated) tb(prj) X ~ 0 (accumulated) o ,k31 D (prj) X o where t = the ctsnulative total air dose due to gama DYair(acctsnulated) emissions for the current quarter plus the release under consideration for the particular reactor unit. l l 0004, Fermi-2 2.0-22 2673W/0051W, 05/24/84

the cumulativa total cir dosa due to beta DScir(cccumulated) cmissions for the current quarter plus the ralcase under consideration for the particular reactor unit. the cumulative total body dose for the elapsed 'D = tb(accumulated) portion of the current quarter plus the release under consideration for the particular reactor the cumulative organ doses for the elapsed portion D (accmulated) = o of the current quarter plus the release under consideration for the particular reactor unit. the number of days into the current quarter to the X = nearest whole day. If activities planned during the remainder of the 31-day period are expected to contrikte a significant dose and the determination can be reasonably made; this contribution should be included in the equations: Dy air (accumulated) 31 + D D Yair(prj) X anticipated 8 air (accumulated) ~' 31 + D Sair(prj) X anticipated U tb(accumul.sted) ~- 31 + D D tb(prj) X anticipated D (accumulated) *'1 o X anticipated o(prj) where D = the anticipated organ dose resulting from anticipated anticipated operational occurrences which may occur in addition to routine releases over the thirty-one (31) day period. l DDCN, Fermi-2 2.D-23 2673W/D051W, D5/24/84

If,' yair(prj) > 0.2 mrad or D8 air (prj) > 0.4 mrad then appropriate portions of the Gaseous Radwaste System shall be used to reduce radioactive materials in gaseous waste prior to their discharge. ~~ If, Otb(prj) > 0.3 mrem or D (prj) > 0.3 mrem o then. appropriate portions of the Ventilation Exhaust Treatment System shall be used to reduce radioactive materials in gaseous waste prior to their discharge. k l OD04, Femi-2 2.0-24 l 2673W/0051W, 05/24/84 l ..,n

TABLE 2.2-1 INHALATION DOSE FACTORS FOR INFANT * (MRD4 PER PCI INHALED) Page 1 of 3 muet set so=E tavaa

v. Doer TNvnDiD ano=Ev Evas si.Lt M

3 h0 Da7A 4.62E-07 4.62E-07 4.62f-07 4.62E-07 4.42E-07 4.62E.07 C 14 1.89E-05 3.?tE-06

3. 79E -0 6 3.79E-06 3.79E-06 S.79E-06 3.79E-06 44 24 7.S4E-06 7.54E-06 7.54E-06 7.54E-06 7.S4E-06 7.54E-06 7.54E-06 P 32 1.4SE-03 0.03E-05 S.53E-Ob NO DATA NO Dafa 40 DATA 1.1SE-05 Ca 51 40 Data MD cafa 6.39E.cs 4.11E-08 9.4SE-09 9.17E-06 2.55E.07 mm S4 NO Data 8 88E-05 3.56E-06 NO Cafa 3.56E-Ce 7.lat-04 S.04E-06 mW 56 40 Daf a 1.10E-09 l.S O E-l O NO Data 7.s4E-10 0.95E-06 S.1FE-05

1. E S5 1.4tE-05 8.39E-06 2.35E-06 NO Data NO Data 6.21E-05 7.82E-07 FE 59 9.69E-06 1.60E-05 6.7TE-06 40 Data 40 Data 7.25E-06 1.??E-05 C0 55 40 DATA 8.7tE-07 1.50E-06 NO Data 40 Data S.55E-04 7.95E-06 CO 60 N0 Data S.73E-06 s.41E-06 40 CaTA NO Data 3.22E-03 2.20E-05 el 63 2.42E-04 1.46E-05 8.29E-06 40 Data 40 Data 3.49E-04 1 73E-06 el 65 1.71E-09 2.03E-10 8.79E-11 40 Data NO Data 5.00E-06 3.SOE-95 CU 64 NO Data 1.34E-09 S.53E-10 40 Data 2.04E-09 6.64E-06 1.07E.e5 29 65 1.38E-05 4.*TE-05 2.22E-05 40 Data 2.32E-05 4.62E-04 3.6?E-OS 24 69 3.95E-11 6.91E-11 5.13E-12 NO Cata 2.87E-11 3.05E-06 9.44E-06 Sa el NO Cata NO Data 2.72E-07 NO Data NO Defa NO DATA (T E-24 pa 84 h0 DATA WO Data 2.s6E-07 40 Data m0 Data 40 Data (T E-24 3

4 Sa Ob 40 Data 40 Data 1.46E-08 40 Data NC Data no DATA LT E-24 28 86 hD Data 1.36E-04 6.30E.05 ND Data 40 Dafa NO Data 2.17E-06 90 se NO DATA 3.90E-07 2.03E-07 40 DATA WO Data he Data 2.42E-07 at 09 40 Data 2.29E-07 3.47E-07 NO cafa 40 Data NO Data 4.tTE-es Sa 89 2.84E-04 40 Data 0.15E-06 NO Oafa m0 Dafa 1.4SE-03 4.STE-05 la 90 2.92E-02 40 Data 1.s5E-03 ho Oafa 40 Data 3.03E-03 9.36E-05 Sa 91 6.83E-08 WO D6TA 2 4 7 E -0 9 40 Data NO Data 3.76E-05 S.24E-05 Sa 92 7.50E-09 NO Data 2.19 E -10 40 Data NO Data 1.70E-05 1.00E-04 T 90 2.35E-06 NO Data 6.30E-08 40 Data 40 Data 1.92E-04 7.43E-05 Y 9tr 2 9tE-10 NO Data 9.90E-12 40 Data no Data 1.99E-06 1 4tE-06 l T 91 4.20 E-D4 40 Data 3 12E-05 40 Defa 40 Data 1.?SE-03 1.02E-05 Y 92 s.17E-te m0 sata 3.29E.30 =0 Data =0 safa n.75E 05 9.04t-05 i Reference 3, Table E-10. i ODCH, Fermi _2 2.0-25 2673W/0051W, 05/24/84 t l

TABLE 2.2-1 CONT'D INHALATION DOSE FACTORS FOR I W ANT * (MREM PER PCI INHALED) Page 2 of 3 5 asutti st.. sone t avEn v.som twva010 sto=Er tvNc st.LL: Y 93 1 07E-07 NO 04Ta

2. 9 t E.0 9 WO Data NO Data 5 46E-0$

1.19E-04 '4a 95 s.24E-0> l.19E-05 1.45E-05 9eo DATA 2.22E-oS 1 25E-03 1.55E-05 24 97 1.07E-07 1.83E-08 8.36E-09 NU 0414 1 05E-08 7.88E-05 3.00E-04 NS 95 1.12E-05 '4.59E-06 2.70E-06 NO Data 3.37E-06 3.42E-04 9.05E-06 NO 99 NO Dafa 1.18i-07 2.3tE-08.NO Data 1.m9E-07 9.63E-05 3.48E-05 IC 99p 9.98E-13 2.0GE-12 2.66E-11 NO Data 2.22E-11 5.79E-07 1.45E-06 TC101 4.65E-14 5.99E-14 5.80E-13 NO Cafa 6.99E-13 4.17E-07 6.03E-07 1 aut03 1.44E-06 NO Data 4.85E-07 NO DATA 3.03E-06 3.94E-04 1.15E-05 4U105 8.74E-10 NO Data 2.9 3 E-10 NO Data 6.42E-10 1.12[-05 3.46E-05 avl 06 6.20E-05 NU Data 7.77E-06 NO Data 7.6tE-05 8.26E-03 1.17E-04 aGt10= 7,13E-06 5.16E-06 3.57E-06 NO Data 7.80E-06 2.62E-03 2.36E-05 IE125m 3.40E-06 8 42E-06 4.70E-07 1.16E-06 NO Dafa 3.19E-04 9.22E-06 7E127P 1.19E-05 4.93E-06 1 48E-06 3.4tE-06 2.60E-05 9.3?f-04 1.95E-05 TE127 1.59E-09 6.8tt-ID 3.44E-10 1.32E-09 3.47E-09 7.39E-06 1.74E-05 TE129* 1.01E-05 4.35E-06 1 59E-06 1.9tt-06 2.27E-05 1 20E-03 4.93E-05 l TE129 5.63E-11 2.48E-11

1. 34 E-11 4.02E-11 1.2bE-10 2.14E-06

1. Set-05 TE131m 7.62L-Os 3.93E-08 2.59E-Os 6.38E-08 1.89E-07 1 42E-04 8.51E-05 TEllt 1 241-11 5.87E-12 3.57E-12 1.83E-11 2.ObE-11 1.47E-06

5. ATE-06 TE132 2.66E-07 1.69E-07

1. 26 E-0 7 1.99E-07 7.39E-07 2.43E-04 1.15E-05 3 130 4.54E-06 9.91E-06 3 9eE-06 1.14E-03 1.09E-05 Mn Data 1 42E-06 I 831 2.71E-05 3 17E-05 1.40E-05 1.06E-02 3.70E-05 ho Data 7.56E-07 I 132 1.21E-06 2.53E-06 8.99E-07 1.21E-04 2.92E-06 NO Data 1.36E-06

) I 133 9.46E-06 1.37E-05 4.00E-06 2.54E-03 1.60E-05 NO Cafa 1.54E-06 I 134 6.stE-07 8 34E-06 4.75E-07 3.10E-05 8 49E-06 NO DATA 9.21E-07 I 135 2.76E-06 5.*3E-06 1.99E-06 4.97E-04 6.05E-06 NO Data 1.3tt-06 C5134 2 83E-04 5.02E-04 5.32E-05 NO Cafa 1.36E-04 5.69E-05 9.53E-07 C1136 3.45E-05 9.6tE-05 3.78E-05 NO Data 4.03E-05 8.40E-06 1 02E-06 C5137 3.92E-04 4.37F=04 3.25E-05 NO Data 1.23E-04 5.09E-05 9 53E-07 C5138 3.61E-07 5.68[-n7 2 84E-07 NO Data 2.93E-07 4.67E-08 6.26F-07 sat 39 8 06E.09 7.03E-13 3.0tE.11 no Data 4.psE-13 4.25E-06 3.64E-05 1 i i J l l j 0D04, Ferini-2 2.0-26 2673W/0051W, 05/24/84

TABLE 2.2-1 CONT'D INHALATION DOSE FACTORS FOR INFANT * (MREM PER PCI INHALED) Page 3 of 3-souctic'E - sowE L 1vt R 7.soor 7mva010 sto=Ev tv=c s!-LLI sa!40 4.00E-05 4.00E-Os 2 07E-06 MO cafa 9.590-09 1.14E-03 2.74E-05 94141 1.12E-10 7.70r-14 3.55E-12 40 DATA 4.64E-14 2.12E-06 3.39E-06 94142 2.84E-11 2 361-14

1. 40 E -12 NO DATA 1.36t-14 1.11E-06 6.95E-07 La140 3.61E-07 1.45t-07 3 68E-Os 40 Osta no caTA 1.20E-04 6.06E-05 LA142 7.36E-10 2.491-10

6. 4 et -11 4D Data N0 caTa D.87E-06 4.25E-05 CE141 1 98E-0) 1.19E-05 1 42E-06 NO Data 3.75t-06

3. 69 F.- 04 1.54E-05 CE143 2.39E-07 1 90E-07 1 59E-03 NO Dafa 4.03E-OS 8.3CE-05 1.55E-05

• E144 2.2SE-03 B.e5E-04 1.26E-04 40 Data 3.e4E-04 7.03E-03 1 06E-04 PR143 1.00E-05 3.74E-06 4.99E-07 40 Dafa 1 41E-06 3.09E-04 2.66E-05 PR144 3.42E-11 1.32E-11

1. 72 E-12 NO Data 4.40E-12 1.15E-06 3.06E-06 N0147 5.67E-06 5.81F-06 3.57E-07 NO DATA 2.25E-06 2.30E-04 2.23E-05 m 187 9.26E-09 6.44E-09 2 23E-09 h0 Da1A NO DATA 2.83E-05 2.54E-05 MP239 2 65E-07 2.3?E-08 1.34 E =0 S NO 041A 4.73L-08 4.2SE-05 1 78E-05

~ i, l i l 1 l 00CN, Fermi-2 2.0-27 2673W/0051W, 05/24/84 .. -..,. _. _ - -. -,,. - -, -. _ -, -....-,, - --.._,__ - ~..

l TABLE 2.2-2 INHALATION DOSE FACTORS FOR CHILD' (MREM PER PCI INHALED) Page 1 of 3 9pCLIDE... SO9E Lgvfa T.00DT TNYROID EIDNEY LUNG GI-LLI l M 3 NO Data 3.04E-Of

3. 04 E-O f 3.04i-01 5.040-07 3 04E-07 3.04E-07 C 14 9.10E-06 1 52E-06 1.82E-06 8 42E-06 1.s2E-06 1 42E-06 1 52E-06 t'

9a 24 6.35E-06 4.35:-06

4. 3 S E -0 6 4.3SE-06 4.35E-06 4 35E-06 4 35E-06

.l P 32 7.04E-04 1.09E-05

2. 67 E-0 5 NO Data NO Data Nn Data 1.t4E.05 Ca 51 NO Data NO Data 4.17E-00 2 31r.08 6.51i-09 4.59E-06 2 93E-07 mN 54 40 Data 1.16E-05 2.57E-0 6 NO DATA 2.7tE-06 4.26E-04 '6.197-06

• N 56 NU Data -

4.48E-10

0. 4 3E-11 NO Data 6.52E-10 3.55C-06 3.33C-05 FE 55 1.28E-05 6.80E-06

2. t C E-0 6 NO Data MD DATA 3.00E-35 7.75E-07 FE 59 5.b9C-06 9.c4E-06 4.5tL-06 NO DaT4 40 Data 3.43[-04 1 91E-05 CD 58 ND paTa 4.T0E-07 8.55E-07 WO Daft NC Data 2 99[-04 9.29E.06 CD 60 NO Data 3.55E-06 6 12 E-0 6 NO Data ND Data 1.9tE-03 2 60E.05 NI 63 2.22E.04 1.25E-05

7. 56E-0 6 NO Data NO Data 7.43E-05 1 7tE-06 NI.45 8."CSE-10 7.99E-It 4.44E-11 Mn Data N!! Data 2 21E-06 2.2?E-05 CU 64 NO Data 5.39E-10 2.90C-10 NO DATA 1.63E-09 2 59E-06 9.92E-06 2.% o b 3.15E 05 3.06E-05 1.90E-05 NO Data 1.93E.05 2 69E-04 4.41E-06 24 69 8.81E-Il 2.6tt-11 2.41L-12 NO Data 1.58E-11 3.84E-07 2.75E-06 mt 81 NO Cafa ND uata 1.2BE-07 Nn Data NO Data No caTa LT E-24 se a4 40 DATA Nu Data 1(4A1-07 No cata NC Data NO Data LT E-24 29 05 NO Data NO Data

6. 8 6 E.0 9 NO Data NG Data NO Data LT E-24 an a6 NO Data 5.36t-05 3 09E.Ds NO CATA NO CATa NO Data 2.16E-06 at 88 40 Data 1.52E-0T 9.90E.08 NO Data NO Data NO Cafa 4.661-09 at 89 NO Data 4.331-06

7. tat.04 NO Data NO Data NO Data 5.llE-10 59 39 1.62E-04 NO Data 4.66E.06 NO Data NO Data 5.01C-04 4.52E.05 Sa 90 2.73E.02 ND DATA 1.74[.0 3 NO DATA NO Data 3.99C 03 9.2st.05 SP 91 3.28E-0B NO CaTa

1. 2 4 E -0 9 NO Data NO Data 1.44E-05 4.70r.05 Sa 92 3 94E-09 NO Data

1. 42 E.10 NO Data NO Data 6.49C-06 6.55E-05 7 90 1 11E-C6 NO Data 2.94E-DS NO Data NC DATA 7.07E-05 7.24E-05 Y 91P 1 1TE-10 NO DATA

4. 9 0 E.12 NO Data NO nata 7.60F-07 4.64E.07 4

y el 2.471-04 NO DATA 6.59E-06 40 Data NO Data 7.10E-04 4.97E-05 7 92 5.50E.09 40 Data 478-10 40 pa7a NO Data 6.46E-c6 6.46E.05 4

• Reference 3, Table E-9.

i ODO4, FerTni-2 2.0 28 2673W/0051W, 05/24/84

TABLE 2.2-2 CONT'D INHALATION DOSE FACTORS FOR CHILD * (MREM PER PCI INHALED) Page 2 of 3 nUCLIDE Sont LivEt . 7.eo0v invaOID alpWEv LugG st-Ett i V 93 5.04E-08 "O OaTA 1 3gE-09 NO 0aT4 NO DaT6 2.01E-05 1.05E-04 2a 95 S.13E-05 1.15E-05 1.00E-05 ND 0416 3 61i-05 6.03E-04 1.65E-05 28 97 5.07E-08 7.34E-09 4.32E-09 NO Da74. 1.05E-08 3.06E-05 9.49E-05 h6 9b 6.35E-06 2.48E-06 1.77E-06 NO Data 2.33E-06 1.66f-04 1.00E-05

1. 0 99 NO DATA 4.66E-06.l.l>E-Os NO Data 1.06E-07 3 66E-05 9.42E-05 IC 99P 4.81E-13.9.41E-13 1.56E-11 no DATA 1.37E-11 2.57E-07 1 30E-06 TC101 2.19E-te 2.30E-14 2.91E-13 NO DATA 3.92E-13 1.5BE-07 4.418-09 Rul03 7.55E-07 NO Data 2.90E-07 NO Data 1.90E-06 1.79E-04 1.2tE-C5 AU105 4.13E-10 NU DATA 1.50E-10 Nn DATA 3.63E-10 4.3nt-06 2.69E-05 Rul06 3 68E-OS NU Data 4.57E-06 40 Data 4.9ff-05 3.87E-03 1.16E-04 AC110- 4.56E-06 3.08E-06 2.47E-36 NO Data 5.74L-06 1.48E-C3 2.71E-05 TE1259 1.82E-06 6.295-07 2.47E-07 5.202-07 40 04T4 1.29E-04 9.13E-06 TE127M 6.72E-06 2.38t-On 8.lut-DT 1.64E-06 1.72E n5 4.00E-04 1.93E-05 TE127 7.49E-10 2.57E-10

1. 6 5 E -10 5.30E-10 1.91E-09 2.71F-06 1.52E-05 1El21r 5.19E-C6 1.85E-06 8.22E-07 1.71E-06 1.16E-05 4.76E-04 4.91E-05 TE129 2 64E-11 9.45E-12

6. 4 4 f -12 1.93E-11 6.94L-11 7.9%E-07 6.09E-06 TE13tr 3.63E-08 1.60E-00 1.37E-05 2.64E-00 1.08E-07 5.56E-05 s.32E-05 TEt31 5.87E-12 2.28E-12 1.7st-12 4.59t-12 1.59E-Il 5.55E-01 3.60E-07 IEt32 1.30E-07 7.36E-08 7.12E-De 8.b8E-08 4.79L-07 1.02E-04 3.72E-05 i L30 2.21E-06 4.4 3 E-06 2 2aE-06 4.99E-04 6.61t-0e NO Data 1.3st-06 j

I 131 1.30E-05 1.30E-05 7.37E-06 4.39E-03 2.13E-05 NO Data 7.6tE-07 I 132 5.72E-07 1.10!-06 5.0FE-07 5.25E-05 1 69E-C6 N0 Data 8.61E-07 1 133 4.40E-06 5.49*-06 2.0SE-06 1.04E-03 9.13E-06 ND 0474 1 40E-06 I 836 3.17E-07 5.04!-07 2.69E-07

1. 7E-05 s.92E-07 NO Data 2.50E-07 i,

I 135 1.13E-06 2.66E-06 1.12E-06

7. 14E-04 3.62E-06 NO Data 1.20E-06 C1134 1.76E-04 2.74E-04

6. 0 7 E -0 5 NO Data 8.93E-05 3.27E-05 1.04E-06 C1116 1.76E-05 4.62E-Ob 3.14E-05 No Data 2.5BE-05 3.93E-06 1.13E-06 I

C5137 2.45E-04 2.23f-06 3.47E-05 NO Data 7.63E-05 2.81E-05 9.7tE-07 C5tas 1.71E-07 2.27E-07 1.50E-07 N0 Data 1.6tE-07 1.84E-08 7.29E-08 eat 39 4.9st-10 2.66F-13 8.4tE-11 NO DATA 2 33E-13 1 56E-06 1.56f-05 .l l l l l-ODCM, Fermi-2 2.0-29 2675#0051W, 05/24/84 l . - -. -a

TABLE 2.2-2 CONT'D INHALATION DOSE FACTORS FOR CHI'_D' (MREM PER PCI INHALED) Page 3 of 3 4 eevCLi nfE. SussE L t 9E8L 7.8007 7N74080 ElDa:E7 LUest St-LLt Dat40 2.00E-Ob 1.75E-00 1.17 E-0 6 k0 Dafa S.71E-09 4.71E-04 2.75E-e5 Delet 5.29E-11 2 95E-14 1.72F-12 MO Cafa 2.56E-14 7.09E-07 7.44E-08 .sa142 1 35E-Il 9.73E-15 7.64E-13 NO Cafa 7.57E-15 4.44E-07 7.4tf-10 La140 1 74E-07 6.08E-08 2.04E-08 NO cafa NO Data 4.94E-05 6.10E-05 La142 3.50E-10 3.IlE-10 3.49E-Il 40 Data NO Data 2.35F-06 2.05E-05 CEt41 1 06E-Ob 5.28E-06

7. 8 3 E-0 F WO DATA.

2.31E-06 8.47E-04 1.53E-05 CEt43 9.89E-08 5.37E-00 7.77E-09 NO Data 2.26E-05 3.12E-05 3.44E-05 CEt44 1 53E-03 5.72E-04 9.77E-05 40 Data 3.17E-04 3.23E-03 1.05E-04 pat 43 4.99E-06 1.50E-06 2 47E-0 7 NO Data S.11t-07 1.17E-04 2.63E-05 Pal 44 1.61E-11 4.99i-12 0.10 E-13 40 Dafa 2.64E-12 4.23E-07 5.32E-08 90147 2.92E-06 2.36E-06

1. 8 4 E-0 7 ND Data 1.10E-06 8 57t-05 2.225-05 w 187 4.41E-09 2.61E-09 1.1TF-09 Mn DATA NC Dafa B.11E-05 2.46E-05 MP239 1.F6E-07 9.04f-0*

4.35E-09 WO Data 2 43E-08 1.57E-05 1.73E-05 I 4 1 l l i 1 0D061, Ferini-2 2.0-30 2673W/0051W, 05/24/84

TABLE 2.2-3 INHALATION DOSE FACTORS FOR TEENAGER * (MREM PER PCI INHALED)- Page 1 of 3 - mutt a ct. sone tevEt f.soCv TNeaolo aloNEv tvNc st-Ett 8s 3 40 0aTA 1.59E-0F

1. 59E -4 7 1.59E-07 1.59f-07 I.59E I.59E-0Y t 14 3.2bE-06 6.C9E-07

6. 09E -0 7 6 09E-07 6.e9E-07 6.09E-07 6.09E-01 ga 24 1.72E-06 3.72E-06 3.72E-06 1.72E-06 1.72E-06 1.72E-06 1.72E-06 9 32 2.36E-04

1. 3 7 J- 0 >

8. 95 E-0 6 40 DATA NC DATA ND Data 1.165-05 Ca 61 ND DATA WD DATA 1.69F-08 9.37E-09 3.84E-09 2.62E 3.75E-07 mW 54 ND DATA 6.39F-06 1.03E-06 ND OATA' I.49E-06 2 48E-04 8.35E-06 NN 56 ND DATA 2.12i-10 3.15E-11 40 Data 2.24E-10 1.90E-06 7.18E-06 FE 55 4 18E-06 2.98E-06

6. 9 3 E -3 7 WD DATA 40 DATA 1.55E-05 7.99E-01 FE 49 1.791-06 4.62i-06 1.79E-06 ND DATA ND DATA 1.91E-04 2.23E-05 CD St ND DATA 2.S9E-07 3.47E-07 ND DATA NO Data 1.68E-04 1.19f-05 CD 60 NO Cafa 1.81E-C6 2.48E-06 WD DaT4 NG DATA 1.09E-03 3.24E-05

+ N16J 7.25E-05 5.43E-06 2.47E-06 NO DATA NO DATA 3.84E-05 1.77E-06 NI 6b 2.73E-In 3.66F-11 1.59E-11 40 DATA ND DAfa 1.17E-06 4.59E-06 CU 64 40 DAfa 2.54f-13

1. 06 E-10 WD DATA 8.01E-10 1.39E-06 7.68E-06 24 65 4.t2E-06 1.o?E-05. 7. 8CE-0 6 ND Data 1 08E-Ob 1.55E-04 5.83E-06 l

EN 69 6.04E-12 1.15F-11

8. 01E-13 ND DATA 7.53E-12 1.98E-07 3.56E-08 1

WR 83 NO DATA N3 DATA 4.30E-06 NO DATA ND Data NO DATA LT E-24 l SR 84 ND DATA No Osfa 5.41E-08 40 DATA 40 DATA WD Data LT E-24 At St NO Dafa N0 cata 2.29E-09 NO CATA ND DATA NO DATA LT E-24 48 86 N0 Data 2.3RE-05 1.05E-05 ND Data 40 DATA ND Data 2.21E-06 RP 88 40 DATA 4.82E-08 3.40E-08 ND Data NO DATA NO DATA 3.65E-15 48 89 ND Data 4.4CF-08 2.91E-08 ND DATA NC DATA NO DATA 4.22E-17 Sa 89 5.43E-05 ND Dafa 1.56E-06 WD DATA NC SATA 3.C2E-04 4.6aE-05 54 93 1.35E-02 ND DATA S.351-04 NO DATA NO Data 2.06E-03 9.56E-05 54 91 1.10E-08 40 CAT A 4.39E-10 NO DATA ND Data 7.59E-06 3.24E-05 54 92 1.19E-c9 NO Cafa 5.c8E-11 Mn Data 40 Data 3.43E-06 1.49E-05 i V 90 3.T3E-07 ND Data 1.00E-08 ND DATA ND Dafa 3.66E-05 6.99E-05 l-Y 91' 4.63E-11 NO Data 1.77E-12 40 Dafa NO Data 4.00E-07 3.77E-09 Y 91 8.26E-05 WD OaTA 2.21E ND caTa WD Data 3.67E-04 5.11E-05 Y 92 1 84E-09 ND Data 5.36E-11 ND Data wD Data 3.35E-06 2.06E-05 ( l I

• Reference 3, Table E-8.

2 0-31 ODCM, Fermi-2 2673W/0051W, 05/24/84 l

.- TABLE 2.2-3 CONT'D INHALATION 00SE FACTORS FOR TEENAGER * (>REN PER PCI INHALED) Page 2 of 3 =Uttsof sone tive9 7.soor 7m aoto atoWEv tv4c cr-tt -.~..~... ........... ~............... Y 93 1 69E-Os 40 Data 4.65E-10 40 Da7a NO Da76 1.04E-05 7.24E-05 ta 95 1 82E-05 5.73E-06

3. 94 E -0 6 NO Data' s.42E-06 3.36E-04 1.86E-05 2a 97 1.72E-08 3 40E-09

1. 5 7 E-0 9 40 Data 5.tSE-09 1.62E-05 7.88E-05 48 95 2 32E-06 3 29E-96 7.Ost-07 NO Data 1.25E-06 9 39E-05 1.21E-05 mD 99 40 Data 2.1tE-08 4.03E-09 NO CATA 5.14E-08 1.92E-05 3.36E-05 7C 99M 1 73E-13 4.5 3E -I l 6.24E-12 NO DATA.

7.20E-12 1.44E-07 7.66E-07 7Ct01 7.40E-15 -1.0SE-14 1.03E-13 NO Data 1.90E-11 'O.34[-08 1 09E-16 eU103 2.63E-07 WO Cafa I.12E-07 NO Data 9.29E-07 9.79E-05 1.36E-05 4U805 1.40E-10 No Data 5 42E-11 NO Data 1.76E-10 2.27E-06 1 13E-05 aut06 ').23E-05 NO Data 1 55E-06 NO Dafa 2.30E-05 2.01E-03 1 20E-04 4C110* 1.73E-06 1 64!-06 9.99E-07 NO Data 3 13E-06 8.44E-04 3 4tE-05 i TE12sp. 6.10E-07

2. ODE-07 8.34E-Os 1.75E-07 40 Data 6.70E-05 9.38E-06 7E127m 2.25E-06 1.CFE-06 2 73E-07 5.4tE-07 8.17E-06 2.07E-04 E.99E-05 rE127 2.StE-10 1 14F-10

5. 5 2 E-11 8.77E-10 9.10E-10 1 40E-06 1.01E-05

\\'1299 1.74E-06 S.23E-07 2 51E-0 7 5.72E-07 6.49E-06 2.47E-04 5.06E-05 TE129 s.87E-12 4.22E-12 2.20E-12 6.4RE-12 3 32E-11 4.12E-07 2 02E-07 IEI31r 1 23E-DO 7.51E-09

5. 0 3 E-0 9 9.06E-09 5.49E-08 2.97E-05 7.76E-05 4

TE131 1.97E-12 1.04E-12 6.30E-13 1.55E-12 7.72E-12 2.92E-07 1.89E-09 TC132 4.50E-Ot 1.e3E-00 2.74E-08 3.07E-00 2.44E-07 5.61E-05 5.79E-05 i I 330 7.80E-07 2.24!-06 8.9eE-07 l.86E-04 3 44E-06 WQ 047a 1.14E-06 3 131 4.43E-06 6.14E-06 3.30E-06 I.03E-03 1.05E-05 NO Da7a 8.11F-07 3 332 1.99E-07 5.47E-07 1 97E-07 1 89E-05 8.65E-07 WO Data 1.59E-07 1 8 133 1.52E-06 2.36E-06 7.78E-07 3 65E-04 4.49E-06 NO Cava 1.29E-06 3 134 l.llE-07 2.90E-07 1 05E-07 4.94E-06 4.5BE-07 h0 Data 2.55E-09 8 135 4.62E-07 1.1SE-06 4.36E-07 7.76E-05 1.86E-06 NO Data S.69E-07 C5134 6.2eE-05 1.4tE-04 6.SeE-05 NO Data 4.69E-05 1.e3E-05 1.22E-06 C5196 6.44E-06 2.42E-05 1.?tE-05 40 Data 1.30E-05 2.22E-06 1.36E-06 C5137 8.30E-05 1.06E-04

3. 0 9 E -0 5 NO Data 3.s0E-05 1.51E-05 1.06E-06 C5138 5.82E-08 1.01E-07 5.5s E -t e NO DATA S.2tE-Os 9.stE-09 3.38E-Il

sa13, 1.67E-10 1.18E-13 4.e7E-12 40 Data s.1 E-13 s.Ost-07 s.06E-07 1

l 2.0-32 000H, Femi-2 l 2673W/0051W, 05/24/84

l l l TABLE 2.2-3 CONT'D INHALATION DOSE FACTORS FOR TEENAGER

• l (MRD4 PER PCI INHALED) i Page 3 of 3

-l i i p 9. 4pCL19E SOME liver T.90DT TM7a010 s10NEY SUNG St-LLI 94140 6.84E-06 S.38E-09 4.40E-07 No cafa 2.SSE-09 2.54E-04 2.86E-95 estet 1.78E-11 1.s2E-14 5.9JE-13 NO caTa 1.23E-14 4.llf-07 9.33E-14 4a142 4.62E-12 4.63E-15 2.84F-13 no Oafa 3.92E-15 2.39E-07 5.99E-20 La140 5 99E-08 2.95E-08 7.8?E-09 NO Data NO cafa 2.6BE-05 6.09E-05 LaE42 1.20E-10 5.31E-11 1.32E-11 ho Oafa 90 DATA 1.27E-06 1.50E-06 CE141 3.55E-06 2 37E-06

2. 71 E-0 7 h0 Data 1.11E-06 7.67E-05 1.58E-05 CE143 3.32E-08 2.42E-00 2.10E-09 NO DATA 1 08E-08 1.63E-05 3.19E-05 CE144 6.11E-04 2.53E-04 3.28E-05 NO Cata 1.51E-04 1 67E-03 1.00E-04 Pal 4) 1 61E-C6 6.64E-07 8.28E-08 No cafa 3.86E.01 6.04E-05 2.67E-05 ra144 5.37E-12 2.20E-12 2.72E-13 90 Data 1 26E-12 2.19E-07 2.94E-14 40147 9.83E-07 1.07E-06 6.41E-08 40 Data 6.28E-07 4.65E-05 2.28F-05 W 187 1.50E-09 1.225-09 4.29E-10 40 Data NO Data S.92E-06 2.21E-05 4*239 4.2sE-os s.99E-09 2.21E-e9

=c saia 1 25E.00 a.11E-06 1 65E-05 0004, Fermi-2 2.0-33 2673W/0051W, 05/24/84 l 'I l ~ -- }

TABLI 2.2-4 INHALATION DOSE FACTORS FOR ADULTS

• t (f4104 PER PCI INHALED)

Page 1 of 3 i Noctic2 sone ts vit 7.nocv Twfap 0.anoNEv tems st.LL: M 3 NO DATA. 1.SSE-07

1. S S E-0 7 1.SSE-t?

3. Set-07 't.SSE-07 1.Sef-07 C le 2 27E-06 4.26E-07 4.26E -0 7 4.26E-07 4.26E-07 4.26E-07 4.26t=07 4A 24 1 28E-06 3 20E-06 1 28 E-06 1 20E-06 1.28E-06 3 28E-06 1.28E-04 P 32 1 65E-04 9.64E-06 6.26E-06 'NO DATA NC DATA Nn DATA 1.00E-05 C# St NO DATA NO DATA. 1 25 E-0 8 7.44E-09 2.tlE-09 1 00E-06 4.tSE-07 mW S4 NO DATA 4.95E-06 7.S I E-O F NO DATA I.23L-06 8 7SE-04 9.67E-06 mM $6 NO DATA 1.55?-10 2 29E-11 NO DATA 3 63E-10 1.f0E-06 2.53E-06 J.

FE $5 3.0TE-06 2.12E-06 4.91E-07 NO DATA NO DATA 9.YlE-06 7.54E-07 FE 59 1.47E-06 S.4TE-Oe 4 32 E-0 6. 40 Data, No DATA t.27C-04 2.35E-05 CD SS NO DATA 1.90E-01 2.S9E-07 NO Cafa NC OAta 1.16E-04 1.53E-05 CD 60 NO DATA 1.44E-06 1 8bE-06 NO DATA NO DATA 7.46E-04 3.96E-05 l NI 63 S.40E-05 3.93E-06

1. Sit-06 NO CaTA NO DATA 2 23E-05 1 67E-06 gt 65 1.92E.10 2 62E-11 1 14F-11 No Data es0 OATA 7.00E-07 1.54E-06 CU 64 N0 CATa 1.83E-10 T.69E-11.NO DA1A S.70E-10 8 4tE-07 6.12E-06 i

l 24 65 4.05E-06

1. 2 9E -05 3.82E-06 40 DATA S.62E-06 1 00E-04 6.68E-06 2

24 69 4.23E-12 0.14E-12 S.65E-13 NO Data 5.27E-12 1.15E-07 2 04E-09 et 33 NO DATA NO Data 3.Olt-OS NO DATA NO DATA NO Data 2 90E-06 Da 84 NO DATA NO Cata 3.91[-08 NO Cata NO DATA NO Dafa 2 0SE.......................................................................... On 85 NO Data NO Data 1 60E-09 NO Cafa NO DATA NO Data LT E-24 1 et to NU Cafa 1.69E-05 7.3fE-06 NO Data NO DaT& NO Cafa 2.00E-06 l 48 Os NO Data 4.84E-08 2.41E-38 NO DATA NO DATA eso caTa 4.tst.19 1 at 89 NO 04Ta 3.20E-00 2.12E-Os NO DATA NO CaTA NO Data 1.16E-21 Se et 3.00E-05 NO D&Ya 1.09E-06 NO DATA NO DATA 1 75E-04 4.37E-05 Sa 90 1.24E-02 N0 Data 7.62E-04 NO cafa NC Data 1.20E-03 9.02E-05 Sa 91 7.74E-09 NO DATA 3 13E-10 NO DATA NO DATA 4.56E-06 2.39E-05 Sa 92 s.43E-In NO cafa 3.64E-11 40 Data NO Data 2 06E-06 S.3eE-06 Y 90 2 6tE-07 NO Da'T A

7. 01 E -0 9 NO Data NO CaTA 2 12E-05 6.32E-05 4

Y gla 3.26E-11 ND caTA 1 2 7E-12 NO DATA NO Data 2.40E-07 1.66E-10 i Y el S.78E-05 NO DATA 1.Slf-0 6 40 DATA NO DATA 2.13E-04 4.SIE-05 l l V 92 8 29E.09 NO Data 3 77E.11 NO DATA No paTa 3 96E-06 9.19E-06 I l Reference 3, Table E-7. 2.0-34 l ODCM, Fermi-2 l 2673W/0051W, 05/24/84 h ~ -.-... - ~. - -, _ - - - - -. - _,. -... - - - -,. - - - - - - -... - - ... _ - - _ - -. -.. -. - _ ~ - -, - ,..-_.r.

TABLE 2.2-4 CONT'D INHALATION DOSE FACTORS FOR ADULTS * (MREM PEP. PCI INHALED) Page 2 of 3 hpCLIDE SONE LivfR T.803T TNTROIO - alpMET LpMC St-LLI Y 93 1.18E-50 NO 04fa 3.26E-10 NO Dafa NO Data e.06E.06 5.27E-05 IA 95 1.34E-05 4.DCE-06 2.91E-06 NO Da7a 6.77E-06 2.21E-04 1.88E-05 la 97 1.21E-08 2.45E-09 1.13E-09 NO Cata 3.71E-09 9.84E-06 6.54E-05 Ng 95 1 76E-06 9.77E-07 5.26E-07 N0 Dafa 9.67E-07 6.31E-05 1.30E-05 ND 99 NO cafa 1.51E-08 2.87E-09 NO Data 3.64E-08 1.'14E-05 3.10E-05 fC 99* 1.29E-13 3.64E-13. 4.6 3E-12 NO Cara 5.52E-12 9.55E-06 5.20E-07 TC101 5.22E-15 7.52E-15 -7.3st-14 40 Data 1.35E-13 4.99E-00 1.36E-21 Aul03 1.91E-07 NO Cata 8.2JE-08 NO Cata 7.29E-07 6.31E-05 1.3eE-05 Aul05 9.88E-11 NO Cata 3.89E-11 NO Data 1.27E-10 1.37E-06 6.02E-06 tul06 8.64E-06 ND 047a 1.0DE-06 NO Data 1.67E-05 1.17E-03 1.14E-04 4G110F l.35'-06 1.25E-06 7.4AE-07 NO Cata 2.46E-06 5.79E-04 3.78E-05 TE1254 4.27s-07 1.9BE-07 5.84E-08 1.3tE-07 1.55E-06 3.92E-05 8.83E-06 TE127* 1.58E-06 7.21E-07 1.90E-07 4.11E-07 5.72E-06 1.20E-04 1.87E-05 i TE127 1.75E-10 0.03E-11

3. 8 7 E-11 1 32E-10 6.37E-10 E.14E-07 7.17E-06 IE129*

1.22E-06 5.64E-07 1.98E-07 4.30E-07 4.57E-06 1.45E-04 4.79E-05 TEl29 6 22E-12 2.99E-12 1.53E-12 4.87E-12 2.34E-11 2.42E-07 1.96E-08 TE131m 8.14E-09 5.45E-09 3 63F-09 6.esE-09 3.86E-08 1.82E-05 6.95E-05 TE131 1.39E-12 7.44E-13 4.49E-13 1.17E-12 5.46E-12 1.74E-07 2.30E-09 TE132 3.25E-00 2.69E-08 2.02E-00 2.37E-08 1.02E-07 3.60E-05 6.37E-05 1 130 5.72E-07 1 68E-06 6.60E-07 1.42E-04 2.61E-06 ho Data 9.6*E-07 1 131 3.15E-06 4.47E-Oo 2.56E-06 1 49E-03 7.66E-06 ho Data 7.85E-07 I 132 1 45E-07 4.07E-07 1.4tE-07 1 43E-05 6.48E-07 NO Cata 5.0BF-08 1 133 1.COE-06 1.95E-06 5.65E-07 2.69E-04 3.2AE-06 NO Cafa 1.11E-06 1 134 0.05E-08 2.16E-07 7.69E-08 3.73E-06 3 44E-07 NO Cafa 1.26E-10 1 135 3.35E-C7 0.73E-07 3.21E-07 5.e0E-05 1.39E-06 NO Cafa 6.56E-07 C5134 4.66E-05 1.06E-04 9.10 E -0 5 NO Da7a 3.59E-05 1.22E-05 1.30E-06 C5136 4.OSE-06 1.83E-05 1.38E-05 NO Data 1.07E-05 1.50E-06 1.46E-06 C1837 5.90E-05 7.76E-05 5.35E-05 NO Da7a 2.781-05 9.40E-06 1.05E-06 C5138 4.14E-08 7.76E-08 4.05E-08 NO Dafa 6.00E-08 6.07E-09 2.33E-13 0a139 1.176-10 8.32E-14 3.4 2 E-12 NO Data T.78E-14 4.70E-07 1.12E-07 l f 00CN, Fertni-2 2.0-35 2673W/0051W, 05/24/84 i . ~ . - _ - _. _, _ _ _. _ _-_ _., _. _. -, - _ _. _ - ~ _

I i TABLE 2.2-4 CONT'D INHALATION DOSE FACTORS FOR ADULTS * (MREM PER PCI INHALED) Page 3 of 3 c l seuCLsut sone E lvEn 7.suor TN7aole aloNEv tvNc s!.tti I 94140 4.tet-06 4.13F-09

l. f! E-0 7 WD Data 2.09E-09 1.59E-04 2 73F=05 eat 41 1.25E-11 9.41E-15 4.20E-13 WD Data 0.75E-15 2.42E-07 1.45E-17 8a142 3.29E-12 3.38E-15 2.07E-Il NO DATA 2.e6E-15 1.49E-07 1.96E-26 Lat40 4.10E-Cf 2.l?E-Os 5.73E-09 NO Cata No cata 1.70E-05 5.73E-05 La142 0.54E-11 3.8BE-It 9.6st-12 NO Data 40 Data 7.91E-07 2.64E-07 CEt41 2.49E-06 1.69E-06

1. 91 L-0 7 NO Data 7.33E-07 4.52E-05 1.50E-05

+ CEt43 2.33E-04 1.72E-Os 1.91k-09 ND Daft 7.60E-09 9.97E-06 2.53E-05 CEt44 4.29E-04.l.19E-04 2.30E-05 NO Data 2.06E-04 9.72E-04 1.02E-04 Pal 43 1.17F-06 4.69E-07 5.89E-03 NO Cafa 2.70E-07 3.51E-05 2.50E-05 PRien 3.76E-12 1.S6E-12 1.91E-13 NO DATA s.61E-13

1. 2 7 F.-0 7 2.69E-te N0147 6.S9E-07 7.621-07 4.56E-os NO DATA 4.45E-D7 2.76E-05 2.16E-05 w 107 1.06E-09 s.85E-ID 3.10 E-10 NO Data NO DATA 3.63E-06 1.94E-05

'.49E-05 me239

.37E.os 2.a2E-09 a.5 5 E.0 9 no Data e.75E-09 4.70E.06 i

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

TABLE 2.2-5' INGESTION DOSE FACTORS FOR IWANT* (MRD4 PER PCI INGESTED)' Page 1 of 3-eeuct t ot sone tavan 7.seve 7mvmoso stoNew tvNc s -Et! M 3 NO DaT6 3.00E-07 3 00E-0 7 3.00E-07 3.08E-07 3 08E-07 3.08E-07 C to 2.3ff-05 5.00E-06 5 06E-06.5.06E-06 5.06E-06 5.06F-06 5.06E-06 Na 24 1.0lf-05 1.Olt-05 1 01E-0 5

1. ORE-05 1.01E-05 1 01E-0S 1 01E-05 P 32 1.70E-03 1.00i-04 6.59E-05 No paTa NO Cata NO Data 2 10E-05 C4 51 NO Data NO DaT a -

1.48E-08 9.20E-09 2 01E-09 3 79E-08 4 11E-01 MN 54 NO Data 1.99E-Ob 4.5tE-06 NO Data 4.4tE-06 NO Data 7 31E-06 l MN 56 40 Data 8.18E-07 1 4 t t-0 7 Nu Data 7.01E-07 NO Data v.43E 05 FE 55' 1.39E-05 0.90E-06 2.40E-06 NO Data NO Data 4.19E-06 1.14E-Os FE 59 3.08E-05 5.sG!-Os. 2 12E-05 NO caTa NO Dafa 1 59E-05 2 57E-05 CD 58 NO Data 3.60E-06 8.93E-06 NO Data NO Data NO caTA S.9ft.06 CD 60 NO Data 1.00E-05 2.55E-05 NO Data NO DATA NO DATA 2.5ff-05 NI 63 6.34E-04. 3.92f-05 2.20E-05 40 Data NO Data NO CATA 1 95E-06 kl 65 4.70E-06 5.32!-07 2 42E-07 NO paTa NO Dafa NO Data 4.05E-c5 Cu to NO DATA 6.09E-0T 2.82E-07 NO DATA 1 03E-06 NO DATA 1 25E-05 JN 65 8.94E-05

6. 's t E- 0 5

2. 91 E-0 5 NO Data 3 06E-05 40 Data 5.33E-05 l

IN 69 9.33E-08 1.68E-0T 1.25E-08 NO Data 6.98E.c8 mn cata 1.315-05 mm 83 Nn Data NO DLTA 3.63E-01 NO Cafa NO Data NO DATA LT E-24 se to NO Cafa M0 Data J.82E-07 NO Cafa NO Cata NO DATA LT E-26 et 89 NO Data NO Data 3 94E-08 NO Data NO Cafa NO Cata LT E-24 eB 86 NO Data 1.10!-04 8.4DE-05 NO Data No cafa No Data 4.35E-06 48 88 kn Data 4.90E-07 2.73E-0T ND Data NO Data Nn cafa 4.8bE-07 80 89 NO Data 2.86E-07 1.97E-37 NO Data No paTA No cafa 9.14E-08 SR 89 2.5IE-03 NO Data 7.20E-05 NO Data NO Cata NO Cafa 5.16E-05 SR 90 1.85E-02 NO Data 4.7tt-03 NO Data NO DATA No cafa 2.31E-04 54 91 S.00E-05 NO Data 1.8tt-06 NO Data NO Data NO Data 5.92E-05 la 92 1.92E-05 NO Data 7.13E-07 NO Data 40 Data NO Caf a 2.07E-04 7 90 0.69E-08 NO CaTa 2.3sE-09 NO Data NO Data NO Data 1.20E-04 V 91= 0.10E-IC NO Data 2.76E-It Nn Data no Data NO Data 2.70E-06 Y 91 1.13E-06 NO Data 3.01E-08 NO Data NO Cata Nn Data 8.10E-05 7 92 7.65E-09 No paTa 2.tSE-10 NO Data NO Data ho Data 1.46E-06 Reference 3, Table E-14. i I ODCN, Ferini-2 2.0-37 t 2673W/0051W, 05/24/84 i I l

4 TABLE 2.2-5 CONT'D INGESTION DOSE FACTORS FOR IW ANT * (MREM PER PCI INGESTED) Page 2 of 3 l Nuct:DE sone tivfa 7.soor Threoso as eNr.v tvWc st-tti V 93 2 43E-08 NO DATA 4.62E-10 NO DATA NO Data-NO Data 1.92E-04 2R 95 2.06E-07 5.02E-08 3.56E-Os.N0 Data 5.41E-08 NO Data 2.50F-05 la 97 1.40E-08.2.54E-09 1.86E-09 NO Cafa 2.56E-09 WO Data 1.62E-04 46 95 4.20E-08 1.73E-Os 3.00E.00 No cafa 1.24E-Ot No caTA 1.46E-05 NO 99 NO Data 3.4CE-05 6.63E-06 NO Data 5.08E-05 NO Data 1.12E-05 IC 99F 3 92E-09 3.96E-09 5.10E.03 Nn Data 4.26E-08 2.07E-09 1.15E-06 IC101 2.27E-09 2.86E-09 2.03E-Ot NO Data 3.40E-08 1.56E-09 4.86E-07 Aut03 1.48E-06 NO Data 4.95E-07 40 04T4 3.00E-06 NO DATA 1.80E-05 RuiOS 1.36E-07 N0 Data 4.5st-Os NO Data 1.00E-06 Nn Data 5.4tE-05 RU106 2.41E-05 ND 0414

3. 01 E-0 6 N0 Data 2.A5E-05 NO Data 1.e3F-04 i

aG110m 9.*96E-07 7.27E-07 4.t!E-07 40 DATA 1.06E-06 NO Data 3.77E-05 IE12br 2.33E-05 7.79E-06 3.1>E-06 7.84E-06 NO Dafa NO Data 1.11E-05 TEt27p 5.05E-05 1.94E-05 7.0fE-06 1.69E-05 1.44E-04 No nata 2.16E-05 TE127 1.00E 06 3.35E-01 2.15E-07 a.14E-07 2.4 4f -06 NO Data 2.10E-05 TE129m 1.00E-0* 3.43E-05 1.5+E-05 3.04E-05 2.50E-04 NO Data 5.97E-05 TE129 2.84E-07 9.79E-Os 6.63E-OS 2.30E-07 7.07E-07 NO Data 2.27E-05 TEI31* 1.b2E-05 6.12E-06 5.05E-06 1.24E-05 4.2tt-05 NO Data 1.03E-04 TE131 1.76E-07 6.50E-08 4.94E-08 1.STE-07 4.50E-07 Nn DATA 7.11E-06 TEt32

2. cat-05

1. 0 3E -0 5 9.6tE-06

1. 5 2 F- 0 5 4.44E-05 Nn Data 3.ttE-05 1 130 6.00E-06 1.325-15 5.30E-06 1 40E-03 1.45E-05 NO CaTa 2.83E-06 1 131 3.59E-05 4.2 3E-05 8.4eE-05 1.39E-02 4.94E-05 Nn cafa 1.5tE-06 I 132 1.66E-06 3.37E-06

1. 2 0 E -0 6 1.5BE-04 3.76E-D6 NO Data 2.73E-06 1 133 1.2SE-05 1.82r-05 5.33E-06 3.3tE-03 2.14E-05 NO Data 3.00E-06 t 134 a.69E-07 1.79E.06

6. 3 3 E-0 7 4.15E-05 1.99E-06 NO Data 1.84E-06 I B35 3.64E-06 7.24E-06 2.64E-06 6.49E-04 0.07E-06 NO Data 2.62E-06 C5134 3.77E-04 7.03E-04 7.10E-0 5 NO Cata 1.stE-04 7.42E-05 1.91E-06 C5136 4.59E-05 1.35E-04 5.04E-05 NO Usta 5.3tE-05 1.10E-05 2.0$E-06 C5137 5.22E-04 6.1 1 E - 04 4.33E-05 NO Data 1.64E-04 6.64E-05 1.91E-06 C$lls 4.StE-07 7.b2t-07 3.79E-0 7 NO Data 3.90E-07 6.09E-00 1.25E-06 84139 8.81E-07 5.94E-10

2. 5 5E -0 8 NO Data 3.51E-10 3.54E-10 5.50!-05 4

i l I 00CM, Ferfi.1-2 2.0-38 2673W/0051W, 05/24/84.

TABLE 2.2-5 CONT'D INGESTION DOSE FACTORS FOR I F ANT * (MREM PER PCI INGESTED) Page 3 of 3 eeUCL fDt SONE liver T.00Df THYn010 EtDNEY 1988C Cl-LLI cal 40 1.71E-04 1.71E-07 s.atf-06 N0 Data 4.06E-08 3.05E-07 4.20E-05 Dat41 4 25E-07 2.91E-10 1.34E-08 NO Data 3 75E-10 1.77E-10 5.19E-06 0a142 8.04E-07 1.53E-10

9. 06E-0 9 NO CaTa s.31E-11 9.26E-It 7.59E-07 Lat40

2. tit-OP 3.32E-09 2 14E-09 NO Dafa NO Oafa NO Data 9.77E-05 Lal42 1.10E-09 4.04E-10 9.6ff-11 NO Data 40 Data NO Data 6.86E-05 CE141 7.OTE-08 4.00E-08

5. 6t t -0 9 NO Cafa 1.4sE-06 NC Data 2.48E-05 Cele) 1.40E-08 9 82E-06 1.17E-09 NO CaTa

2. tee-09 NO Data 5.73E-05 CEt44 2.90E-06 1.22E-06 3.67E-07 NO Cata 4.93E-07 NO Data 1.7tE-04 94143 9.13E-08 3.c4E-00 4.03E-09 NO Cafa 1.13E-ne NO Data 4.29E-05 Pat 44 2.74E-10 1.06E-10 1.38E-!!

NO Data 3.R4L-ll NO Data 4.93E-06 Note? 5.53E-CB 5.6BE-08

3. 4 s t -0 9 WO Cafa 2.19E-0A NO cafa 3.60E-05 W 187 9 03E-07 6.2se-07 2 17E NO Cafa NO CaTa NO Data 3.S9E-05

................................_-07...................................... WP239 1.llE-OS 9.93E-10 5.6 t f-10 40 paTa 1.98E-09 NC cafa 2.8 7f =05 1 l l l ODCN, Femi-2 2.0-39 2673W/0051W, 05/24/84 t ~. .~

TABLE 2.2-6 INCkSTION DOSE FACTORS FOR CHILD' -.(MRF.M FER PCI INGESTED) Page 1 of 3 l muCL f>F DONE LIFit' T.sDur TNiaDID alD4tv LUNC St-LLI N 3 NO Data 2.03E-07 2.Olf-07 2.03E-07 2.93E-07 2.03E-07 2.03E-07 C to 3.23E-05 2.=2E-06 2.42E-06 2 42E-06 2.42E-06 2.42E-06 2.42E-06 Na 24 b.00E-06 5.00E-06 5.8CE-06 5.93E-06 5.80E-e6 5.00E-06 5.80E-04

• 32 0.25E-04 3 06E-05 3.ltE-05 NO DATA NO Data NO Data 2.28E-05 CR 51 NO Data NO Cafa 0.90E-09 4.94E-09 3.35E-09 9.02E-09 4.72E-07 NN 54 NO DATA 1 0TE-05 2.85E-06 NO UaTa 3.00E-06 40 0414 8.98E-06 NN $6 ND Defa 3.34E-07 f.54E.08 NO CATA 4.04E-07 NO DATA 4.84E-05 fE SS 1.tSE-05 6 10E-06 8 895-06 NO Data NC DaT A 3.45E-06 1.83E-06 FE $9 1.6st.05 2.67E-05 1.34E-05 NO Data NO Data 7.74E-06 2.78E-05 CD $5 40 Data 1.80E-06 S.5IE-06 NO Data NO Data NO Dafa 1.0$E-CS 1

CD 60 no 041a

5. 2 9 F - 06 1 56E-05 NO Data 40 DATA NO Data 2.93E-05 NI 63 5.38E-C4 2 80F-05 1.83E-05 NO Data NO Dafa NO Data 1.94E-06 NI 65 2.22E-06 2.09F-07 1 22E-07 Nn Data NO Data NO Data 2.56E-05 Cu 64 NU Data 2.45E-07 1.4tE-07 NO 0414 5.92E-07 WO Dafa 8.tSE-05 2N 65 1.37E-05 3.65E-03 2.2TE-05 40 Data 2.50E-05 Nn Data 6.4tE-06 AN 69 4.38E-08 6.s3E-08 5.25E-09 NO Data 3.84t-08 NO Data 3.99E-06 en SJ NO Data NO Data 1.ftE-07 NO Data NO Data NO Data LT E.24 Sa 84 NO Data NO Data 1.95i-07 NO Data NO Data NO Data LT E.24 i

Am 85 NO Data NO Data 9 32E.39 NO Data NO Data NO Data LT E.26 l as so No Data 6.10 E- 0 5 4 12E-05 NO Data NO Data Nn Data 4.318-06 1 88 88 NO Data 1 90E-07 1.12E-07 NO Data 40 Data NO Data 9.32E-09 Rt 89 NO Data 1.1TE-07 1.04E-DT NO Data NO Data NO Defa 1.02E-09 la 89 3.32E-03 NU cafa 3.77E-05 NO Data NO Data NO Data 5.81E.01 SR 90 1.70E-02 No cafa 4.3tt.03 NO Data NO Data NO Data 2.29E.c4 SR 91 2.40E-05 NO Data 9.06E-07 NO Data NO Data NO Data 5.30E-05 54 92 9.03E-06 NO Data 3.62E-07 40 Data NO Data NO Data 1.ftE-0* Y 90 4.!!E-00 40 Data 3 10E-09 NO Data 40 Data NO Data 1.lft-06 Y 917 3.82E-10 NO Data 1 31E-! ! h0 Data NO Data Nn Data 7.4eE-27 T 93 6.02E-07 NO Data 4 6tt-05 NO DaT4 40 Defa Nn D414 8.02E-05 Y 92 3.60E-01 NO Data 3.0 AE-10 NO Data NO DATA NO Data t.06E.06 1 I i Reference 3, Table E-13. 2.0-40 ODO4, Fermi-2 2673W/0051W, 05/24/84

I 3m m a i:TWl.E 2.2-6 CONT'D INGESTION DOSE FACTORS FOR CHII.f\\',.]s p s 1(MREM PER PCI INGESTED) M. 1 s w q: 4 Page 2 of 3 '.y y + A g. g 4'N 1, 5 } a q i 'N g 't 4 r c WUCLIDE 00'et LivEt ,T.000f TMvt010

K10hEv,

'LIMeC GI-LLI i NO DATA

1. 0 Daft }#C OATA ' t.73!-04

,013E-1E') 20 Da? A - v '93 3.14E-05 NO DATA' 2.'2 7 E -0 0 3.65E-08 wo Data, 2.66E-05 2R 95 1.16E-07 ~ 2. 3 2 f-08 2R 97 6 991-09 1.01E-09.b.9&E-AO' ND DATA 1.45L.09 NO DATA 1.53E-04 ................................a.......................................:... ees 95. 2.'t S E-0 8 0.76E-0/ 6.26E.09 esO Da74 8.23E-09 eso Cafa 1.62E-05 3 s'D 99 se0 Data I.33E-r5

• 3.2 9E-06 NO DATA 2.84E-05 NO Data 1 10E-05 1

l1*. 99" 9.23E-10 1.81E-09 3.0DE-03 a:0 Data 2.63E-08 9.19E-10 1.03r-06 s! I FClot 1.07E-L'9 1.12i-09 1.'42 E-NE se0 DATA 1.2f1E-0R 5.92E-10 3.56E-69 4 89103 7.31E-07 N@ DAfa 2.01E-07 NO DATA 1 84E-06wo cara 1.s9E-0!w P.U105 6.45E-08 toD esfA 2.34E-Og se0 DATA 5.67E-07 No' Data 4 211 45 '\\ S ($ RU106 1 17E-05 aso Cafa 1 46E-06 se0 DATA 1 5BE-05 800 DATA 1 82E-04 5 'AG110M 5.39E-07 3.64E-07 2.91E-07 ND DATA 6.78E-07 NO DATA 4.33E-05 4 TE125M 1.14E-05 3.09E-06

1. 5 Z E -0 6 3.20E-06 40 DATA NO 6tta 1 105-05 TElffm 2.09E-05 7.78E-06 3.4sE-06 6.91E-06 E.24E-05 NO DATA 2 34E-c5 T E 11,7 4.71E-07 1.21F-07 1.01E-07 3.26E-07 1 14E-06 Nn Data 1 34E-05 4

IE129 4.87E-05 1.36E-05 7.5et-06 1 57E-05 1.43E-04120 Data 5 94E-05 ....J.".................................................... y T E 120 1.34E-07 3.74E-08 3.18E-Os 9.56E-38 3 92E-07 -NO Data 8.34E-06 TE131m 7.20E-06 2.492-06 2.65E-06 5.12E-06 2 41E-05 NO Data 1 01E.04 TE131 8.30E-CB

2. 5 3E- 0 5 2.47E-08 6.35E-De 2.51E-07 NO GATA e.36E=07 j

J TE132 1.01E-05 4.47E-Co 5.40E-06 6.51E-06 4 15E-05 V.*OJTA 4.5 0 E-35 ^ s 1 130 2.92E-06

5. 9 0E-06 F.04E-06 6.50E-04 8.82E-06 NO CATA 2 76E-06

......................................................$.5,N3 Da A........T....1 4 4 F,- 0 6 1 131 1.72E-05

1. 7 3E-05 9.sJE-06 5.72E-03 2.84E-I 132 0.00E-07 1.47E-06 4.76E-07 6.82E-05 2.25E.06 sen oat A 'x1.7E 06 8 131 5.92C-06 7.e2E-06 2.77E-06 1.36E-03 1 22' DS mHO OffA' 2 95E-06 ; {

3 136 4.19E-07 7.78E-07 3.5BE-07 1.73E-05 1.19E-OLM Hn Daf& 5.1. !-O r i 4 ...............................................................,.4......... 8l 8 135 1.75E-06 3.15E-06 1.49E-06 2.79E-04 4.93Ea06 NO Dat h 2 d SF-06 ? C5136 2,. 34 E -t

• 3.84E-04 8.'10 E-0 5 aso cafA 1.1%E.04 4.27E-05 W 37E-06

~ C5136 2.h5E-05' 6.4 6E-05 4.18E-05 NO DATA 3 44E-05 5.13E-06 @ 77E-06 C5t3r 3.2 7f-04. 3.13E-04 4.62E-05 soo Data 1.526-04 3 67E-05 J.96E-06 CSf 38, 2.261*07 3.17E-07 2.01E-07 NO DATA 2.23E-07 2.40E-OS 1.46E-07 Da13% i.14E-07 2.21E-10

1. 20E -t e soo DATA 1.93t.10 1.10E-10 2.19 E-0 5 I

s 7 f I r l s b J .g +. g i ~. g

• (

\\.' \\ 3 L \\,, . Y n s i y "1 ' u- ,1 ) (), ) g\\ s 3 s x s s ODCN, Fermi,2 2.0-41 4y + s 2673W/0051W,'05/24/84 j rs [j N 3 s s t' 4 4 5 >, ;, y( ww .. -, - -, ~ -. - - - - -.--.------ ---,----- L d +, - - --- - - ~~~~

TABLE 2.2-6 CONT'D INGESTION DOSE FACTORS FOR CHILD' (MREM PER PCI INGESTED) Page 3 of 3 uuCL IWE SOME LIVEa

• f.e007 fnfa0IO EIONEY LUNG GI-LLI

.........................a............... Batte 0.JtE-05 T.20E-Og 4.0$E-96 NO Da7a 2.37t-08 4.34E-08 4 2tE-05 Sat 41 2.00E-07 1.12 -10 6.htE-09 NO Ca74 9.69E-11 6.SBE-10 1 14E-07 Sa142 8.74E-08 6.29E-11 4.88E-09 MO OafA S.09E-11 3.70E-11 1 14E-09 L4140 8.01E-OP -3.53E-09 1.11E-09 NO DAfa NO CATA NO DATA 9.04E-05 L4142 S.74E-10 1.67E-10 S.23!-11 NO DATA NO O&fa NO DATA 3.31E-05 CE141 3.97E-CA 1.98E-00

2. 94 E-0 9 NO CaTA 8.68E-09 NO DATA 2.47E-05 CE14J 6.99E-09 3.79E-06 5.49E-10 NO DATA 1.59E-09 NO DATA 5.55E-05 CElse 2.00E-06 -6.52E-0T 3.IBE-07 NO DATA 3.616-07 NO Data 1.70E-04 Pate) 3.93E-08 1.let-08 1.95E-09 NO DATA 6.19E-09 NO DATA 4 24E-05 P4144 1.29E-10 1.91E-18

6. 4 9E-12 NO DATA 2.11E-11 NO DATA g.59E Note?

2.7 9 E-C A 2.26E-08 1.75E-09 NO Cafa 1.24E-08 NO DATA 3.58E-05 W 187 4.29E-07 2.54f-07 1.14E-07 Nu DATA NO Data NO DaT4 3.575-05 NP239 5.2bE-09 3.77E-10 2.6bi-10 No caTA 1.091 09 NO DATA 2.79E-05 I r l ODCM, FerTni-2 2.042 2673W/0051W, 05/24/84

TABLE 2.2-7 INGESTION DOSE FACTORS FOR TEENAGER 0 (MREM PER PCI INGESTED) Page 1 of 3 eeUCL ICE SONE LIVEt 'T.00cv TNytotD alpWEY LUNC 61.Lt1 ~ A 'M )* * *NO D AT a 1.06E-07 1 0et-07 1 06C-07 1.96E-07 1.06E-07. 1 06E-07 C 14 4.06E-06 8.12f-07 8 12 E-0 7 8.12F-07 8.12E-07 8.12E-07 0.12F-07 Na 24 2 50E-06 2.30E-96 2 30E-06 2 30E-06 2.30t-06 2 10E-06 2.30E-06 F 32 2 76E-04 1.71E-05 1 07E-05 ND DATA NO Data NO DATA 2.32E-05 6.05E-0 F C# 51 NU OAfa NO Data 3.60E-09 2 00E-0? -1.89E-10 5.14E-09 ~ 1 21E-05 PN 54 NO Data 5.90E-Oe 1.1?E-06 ND DATA 1.76E-06 NO Data NN 56 NO DATA 1.38E-01 2.81E-08 NO Data 2.00E.07 NO DafA 1.0aE-05 f f 53 3 78E-06 2.68f=06 6.25E-07 No DATA NC DATA 1.70E-06 1.16E-06 FE 59 5 81E-06 1.s7E-05 5.29E-06 NO DafA NO DATA - 4.32E-06 3 24E-05 CD 58 NO Data 9.72E-07 2.24 E-0 6 NU DafA NO DATA MO Data 1.34E-05 CU 60 NO DafA 2.C1E-06 6.13E-0 6 NO DafA NO DATA NO Data - 3.66E-05 N163 1 1?E-04 1 25C-05 e.0DE.06 NO DATA NO DafA NO Data 1.99E-06 gl 65 7 49E-07 9.b7E-08 4.36E-08 NO DAfa 40 DATA NO DATA 5 19E-06 CU 64 NO Data 1 15E-07 5.41 E-0 8 WO Cafa 2.91E-07 NO DATA 8.92E-06 24 6b 5.16E-06 2.COE-E5 9.11E-0 6 NO UATA 1.28E-05 No Data 8.47E-06 .................................................................. 5.16E-08 AN 69 1 47E-08 2 60E-08 1 96E-09 NU DATA 1.m)E.08 No DATA Bt 83 NO Data NO D AT A 5.74E-08 NO Data NO Data NO Data Lt E-24 Sa 84 No Data ND Cafa 7.22E-08 ND Data NC Data NO Data LT E-24 et 8% NO Data 40 Data 3 05E-09 NO DATA NO DATA No Da1A L1 E-24 ES 86 NO Dat a 2 40E-05 1 40E-05 ND Data NO DafA NO Cata 4.41E.06 48 88 NO Data 8.52E-OR 4.56E-08 NO Data NO Data NO Data 7.30E-15 N8 89 NO Data 5 50E-08 3 89E-06 NO DATA NO DATA NO Data 8 43F-17' la 81 4.40E-04 NO D AT A 1 26E-0 5 NO DATA NO Data NO Data S.24E-05 14 90 8 30E-03 ND Data 2 05E-03 NO DATA NO Data NO Dat a 2 33E-04 ............................................................................3 66E-05 54 91 S.C7E-06 NO Data 3 21E-07 No Data NO D AT E NO Data 54 92 3.05E-06 NO Data 1 30E-07 NO DafA NO DATA ND DATA .7.71E-05 l Y 90 1.37E-08 NO DATA 3 61E-10 NO DATA NO Data NO DATA 1.13E-04 l .........................................................................6.09E-09 V 91> 1.2*E-10 NO DATA 4.93E-12 NO Data NC DATA NO Data Y-91 2 01E-07 NO Data

5. 59E-0 9 NO DATA NO Data Nn Dat a 8.24E-05 Y 92 1.21E-09 NO Data 3 50E-11 ND DAf a NO Data No Data 3 32E-05 i

Reference 3, Table E-12. i 2.0-43 0D04, Fe2fni-2 2673W/0051W, 05/24/84

• • • f
• ' - + +
• r,

TABLE 2.2-7 CON 1'D INGESTION 00SE FACTORS FOR TEENAGER * (WlEM PER PCI INGESTED) Page 2 of 3 sone tsvEn T.s00v favect0 steNEv Lows st-tt aucEspf .v 93 3.e3E.c9 NO Cat a s.0$E-10 NO Data No paTA No Da7A 1 11E-04 2a 95 4.12E-On 1.30E-08 S.9*E-09 NG Data 1.91E.c4 WO Data 3 00E-05 2 37E-09 4.69E-10 2.16E-10 NO Data 7.llE-10 NO Caf a 1 27E-04 .tt 97..... me 95 8.22E-09 4.561-09

2. 51E -0 9 NO Dafa 4.42E-09 No cafa I.95E-05

1. 0 99 40 0414 6.03E-06 1 15E-0 6 No cafa 1 3sE-05 NO Data 1 08E-05 IC 99m 3 12E-10 9.265-10 1.20E-Os NO Cafa 3 3sE-ne 5 14E-10 4.Ost-07 7C101 3.60E-10 5.12E-10 5.03E-09 Mn Data 9.26E-09 3.12E-10 8.75E-If tulo)..t.55E-07 NU Data 1.09E-07 NO Data s.99E-07 Nn Dafa 2 13E.05

( sW105 2.18E-04 No pata 8.46E-09 NO pafa 2.7 5E-07 NO DATA 1 76E-05 aut06 3.12E-06 NO Cafa 4.14E-07 NO Dafa 7.56E-06 NO CaTa 1.88E-04 60110* 2 05E-07 1.94E-07 1.taE-07 NO Data 3 70E-07 ho Data 5 45E-05 TE125m 3.83E-06 1.30E-06 5.12E-07 1 0 7E-J6 NO Cais NO Cara 1.13E.05 7E127m 9.67E-06 3.4sE-06 1 15E-06 2 30E-06 3 92k-05 No DATA 2.4tt-c5 FE127 1 5BE-07 5.60E-08 3 40E-08 1 09E-07 6 40E-07 NO Daf t 1.22E-05 IE129m 1 63E-05 6.05f-06 2.5eE-06 5.26E-06 6.42E-05 Nn Data 6.12E-05 7E129

• .4BE-09 1 6?F-08 1.01E-08 3 20E-08 1 38E-07 ND Data 2 45F-07 TE13tm 2.44E-06 1 17E-06 9.76E-07 I.76E-06 1.22E-05 NO Cafa 9.39E-05 TE131 2.79E-08 1 15E-05 8.72E-09 2 15E-00 1 22E-07 NO Data 2.29E-09 TE132 3 49E-06 2 21E-06 2 06E-06 2 33E-06 2 12E-05 No cat a 7.00E-05 3 130 1 03E-06 2.90E-06 1 19E-06 2 43E-04 4.59E-06 NO Data 2.29E-06 8 131 5.0bE-06 8.11E-06 4.40E-06 2.39E-03 1 41E-05 NO Data 1 62E-06 I 332 2.79E-01 7.30E-07 2 62E-07 2.46E-05 3 15E-06 ND Data 3.1st-07 8 133

-2 0tt-06 3.4tE-06 1 04E-06 4.76E-04 5.98E-06 NO Da74 2.5st-06 I 134 1 46E-07 3.87E-07 1.39E-07 4.45E-06 6.10E-07 'NO Cata 5.10E-09 I 135 6.10E-07 1.57E-06 5.82E-07 1.clE-04 2.40E-06 NO Cafa 1.74E-06 C5134 8.37E-05 1.97E-04 9.14E-05 NO Data 6.26E-05 2 39E-05 2.45E-06 C5136 8.59E-06 3.30E-05 2 27E-D5 NO DATA 1.34E.05 2 90E-06 2.72E-06 CSI37 1 12E-04 1.49E-04 5.19E-05 NO Da7a 5.07E-05 1.97E-05 2.12E-06 C5338 7.76E-08 1.49E-07 7.45E-Os No Data 1 10E-07 1 28E-05 4.76E-It 84139 1.39t-07 9.TSE-11 4.0SE-09 NO Data 9.22E-Il 6.T4E-t! t.24E-06 l l 2.0-44 0004, Fermi-2 2673W/0051W, 05/24/84 j

TABLE 2.2-7 CONT'D INGESTION DOSE FACTORS FOR TEENAGER * (MREM PER PCI INGESTED) Page 3 of 3 i 9pCLIEE DONE LIVER Y.000f To VacIO RIO4EY LUNC St-LL1 ...... 4............... 04140 2.84E-05 3.4RE-OS

1. t BE-0 6 40 OATA 1.18E-00 2.14E-08 4.3tE-05 04141 6.71E-On 5.n1E.11 2.24E-09 40 DATA 4.65E-11 3.43E-11 1.43E-13 OA142 2.99E-00 2 99E-11

1. 84 E-0 9 40 DATA 2.53k-11 1.99E-11 9.18E-20 La140 3.4tt-09 1.71E-09

4. 5 5 E-10 40 DATA NC OATA NO DATA 9.82E-05 Lal42 1.79E-10 T.95E-11 1.9st 11 NO DATA 40 DATA ho DATA 2.42E-06 CE141 1.33E-08 8.80E-09 1.02E-09 40 DATA 4.18E-09 ho DATA 2.54E-05 CE143 2.35E-09 3.71E-06

1. 91 E-10 NO DATA 7.67E-10 ho CATA 5.14E-05 CEles 6.96E-07 2.88E-07 3 74E-08 WO DATA 1.72E-07 40 DATA 1.75F-04 Palos 1.31E-08 5.23E-09

6. 52 E -10 40 DATA 3.94E-09 40 DATA 4.31E.05 PRl44 4.30E-11 1.76E-11 2 18E-12 NO DATA 1.01E-11 NO DATA 4.74E-14 4014T 9.18E-09 1 02F-08 4.11E-10 h0 DATA 5.99E-09 kn DATA 3.6BE-05 b 187 1.46E-07 1.19E-07 4.1FE-38 WO DATA 40 DATA NO DATA 3.22E-05 4P239 1.76E-09 1.66E-10 9.22E-11 NO DATA S.21E-10 no DATA 2.67E-05 i

l I l I l ODOH, Fermi-2 2.0-45 2673W/0051W, 05/24/84 L

TABLE 2.2-8 INGESTION DOSE FACTORS FOR ADULTS * (MREM PER PCI INGESTED) Page 1 of 3 meCL,lDE 804t L ivER f.SOCT TNTROID RIDNEY LUNC GI-Ltl-H 3 40 DATA 1 05E-07

1. 05 E -0 7 1.05E-07 1 05E-07

1. die-07 1.05E-07 C 14 2 04E-06 5.6tE-07 5.6 8 E-0 7 5.65E.07 5 6sE-7f 5.6eE-07 5.60E-07 1

NA 24 1.70E-06 1.70E-06

1. 70 E-0 6 1.TCE-06 1 70E-Oo 1.70E-06 1.70E-06

) P 32 1.93E-04 1.20E-05

7. 4 a E -0 6 90 DATA NC DATA NO DATA 2.17E.05 CR 51 NO DATA NO DATA 2.6eE-09 1.59E-09 5 86E-10 3.53E-09 6.69E-0T P.4 54 NO DATA 4.57E-06 0.72E-07 NO Data - 1 36E-06 NO DATA 1.40E-05 NN 56 NO DATA 1.155-07 2 04E-04 NO DATA 1 46E-07 NO DATA 3.67E-06 FE 55 2.TSE-06 1.90F-06 4.43[-07 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.BSE-06 3.40E-05 CD 50 NO DATA 7.45d-07 1.67E-06 40 DATA NO DATA NO DATA

!.51E-05 CD 60 NO DATA 2.14f-06 4.72[-06 NO DATA NO DaIA-- 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 6.06E-08 3.13E-Ce 40 DATA NO DATA NO DATA 1.74E-06 CU 64 NO DATA 8.33E-08 3.9tE-08 NO Data 2.10E-07 kn DATA ~7.IDE-06 2N 65 4.84E-06 1.54E-05

6. 9.E -0 6 NO DATA 1 03E-05 NO DATA 9.70E-06 2N 69 1.03E-08 1 91[-08 1.37E-09 40 DATA 1.28E-os NO DATA 2.96E-09 OR 83 NO DATA NO Data 4.02E-05 40 Data No Data NO DATA 5.79E-OS OR 96 NO Data NO DATA 5.2tE-08 ND DATA NO DATA NO DATA 4.09E-13 OR 85 NO DAT A NO Data 2.14E.09 NO Data NO DATA NO DATA LT E-24 R8 86 NO DATA 2.!!E-05

9. 8 3 E-0 6 Nn DATA NO DATA NO DATA 4.16E-06 RB 88 NO DATA 6.051-08

1. 2 t E -0 8 NO DATA NO DATA NO Data s.36E-19 El 89 NO DATA 4.01E-08 2 82E-04 NO DATA NO DATA NO Data 2.33E-21 5R 89 3.00E-04 NO DATA 8.0*E-06 NO DATA NO DATA NO DATA 4.94E-05 54 90 7.5BE-03 NO DaIA 3 86E-03 NU DATA NO DATA NO DATA 2.19E-04 Sa 91 5.6TE-06 NO Data 2.20E-0 7 NO DATA NC DATA NO Data 2.70E-05 SR 92 2.15E-06 NO DATA 9.30E-08 NO Data NC Data NO DATA 4.26E-05 Y 90 9.62E-09 NO D,ATA

2. 5 8 E -10 40 DATA NO DATA NO D AT A 1.02E-04 Y 91m 9.09E-11 NO DATA 3.52E-12 NO DAfa NO DATA NO DATA 2.67E-10 V 91 1 41E-07 40 DAfa 3.77E-09 NO DATA NO Data NO Data 7.76E-05 Y 92 S.45E-10 NO Data 2.47E-11 NO DATA NO DATA NO DATA 1.4BE-05 i

I i \\ l I Reference 3, Table E-11. l l 1 ( CDCN, Fermi-2 2.0-46 2673W/0051W, 05/24/84

TABLE 2.2-8 CONT'D INGESTION DOSE FACTORS FOR ADULTS * (MREM PER PCI-INGESTED)- Page 2 of 3 .~. NUCE l J. SONE L1Vta - T.000T TNYROIC EIDNEY LUNG St-LLI 0 Y 93 2.68E;09 NO DATA 7.40E-11 NO DATA NO DATA NO DATA s.50E-05 2R 95 3.04E-08 9.75E-09 6.60E-09 NO DATA 1 53E-08 NO DATA 3.09E-05 la 97 1.6BE-09 3 39E-10 1 55E-10 NO DATA 5.12E-10 NO DATA-1.05E-04 48 95 6.22E-09 3.46E-09

1. 86 E-0 9 NO DATA 3.42E-09 NO. DATA 2.10E-05 NO 99 NO DATA 4.31E-06 8.20E-07 NO DATA 9.76E-06 NO DATA 9.99E-06 TC 99N 2.47E-10 6.9BE-10 d.09E-09 NO DATA 1 06E-Os 3.42E-10 4.15E-07 TC101 2.54E-10 3.66E-10 3.59E-09 NO DATA 6.59E-09 1 57E-10 1.10E-F1 RU103 1 85E-07 NO DATA 7.97E-08 NO DATA 7.06E-07 NO DATA 2.16E-05 RU105 1.54E-05 NU CATA

6. 00 E -0 9 NO DATA 1.99E-07 NO DATA 9.42E-06 aut06 2 75E-06 40 DATA

3. 4 s t-0 7 No DATA 5.31E-06 NO DATA 1.78E-04 AG110M 1 60E-07 1 40E-07 0.79E-Os 90 DATA 2.91E-07 NO DATA 6.04E-05 TE125m 2 65E-06 9.71E-07 3 59E-07 8.06E-D7 1.09E-05 NO DATA 1.07E-05 TE127*

6.77E-06 2 42E-06 s. 2 5 E -0 7 1.73E-06 2.75E-05 NO DATA 2.27E-05 TE127 1.10E-07 3.95E-CB 2 3sE-00 0.15E-08 4.4tE-07 NO DATA 8.6BE-06 TE129" 1.15E-05 4.29E-Co 1 82 E-0 6 3.95E-06 4.80E-05 NO DATA 5.79E-05 TE129 3.14E-00 1 18E-05 7.62E-09 2.41E-08 1.32E-07 NO DATA 2.37E-08 TE131m 1 73E-06 8.'6E-07 1 05 E-0 7 1.34E-06 8.57E-06 NO DATA e.40E-05 TEl31 1 97E-08 8.23E-09

6. 2 2 E-0 9 1.62E-Os e.63E-OS NO DATA 2 79E-09 TE132 2.52E-06 1 6)E-06

1. 5~sE-0 6 1 00E-06 1.57E-05 NO DATA 7.71E-05 1 130 7.56E-07 2.2 3E-06 8.00E-07 1.89E-04 3.40E-06 No DATA 1 92E-06 4

I 131 4.16E-06 S.95E-06

3. 41 E-0 6 1 95E-03 1.02E-05 NO DATA 1.57E-06 1 132 2.03E-07 5.43E-07 1.90E-07 1 90E-05 8.65L-07 NO DAT A 1.02E-07 1 133 1 42E-06 2.4TE-06 7.53E-07 3.63E-04 4.31E-06 NO DATA 2.22E-06 I 134 1.06E-07 2.88E-07 1 03E-07 4.99E-06 4.5BE-07 NO DATA 2.5tE-10 1

I 135 4.43E-07 1.16E-06 4.2eE-07 7.65E-05 1.86E-06 NO DATA 1 31E-06 C1134 6.22E-05 1.48E-04 1 2tE-04 NO DATA 4.79E-05 1 59E-05 2 59E-06 C5136 6.51E-06 2.57E-05 1 85E-05 40 DATA 1.43E-05 1 96E-06 2 92E-06 C5137 7.975-05 1.09E-04 7.14E-05 No DATA 3.70E-05 1 23E-05 2.llE-06 C5138 5 52E-08 1.09E-07 5.40E-Os NO DATA S.01E-08 7.91E-09 4.65E-83 SA139 9.70E-08.6.91E-11 2 04E-09 NO DATA 6.46E-11 3 92E-11 1.12E-07 t i i l i 1 0D04, Fermi-2 2.0-47 2673W/0051W, 05/24/84 \\

TABLE 2.2-8 CONT'D INGESTION DOSE FACTORS FOR ADULTS * (MREM PER PCI INGESTED) Page 3 of 3 soNt Livet v.a00r TNvA0le slowty twec st.Ltl mutt 10L., sA140 3 0st.05 2.sst-Os 1.3 st-o 6 =0 OATA s.676 09 1 46E-Os

4. tee-05

) malet 4.11E.08 9.b6t 1.59E.09 40 DATA 3.31E.11 2.02E.11 2.22E-17 2 1sE.0e 2.19E-11 1 34E.09 NO DATA 1.e5E.11 1 24E-11 1.00E.26 ,oA142 LA140 2 90L-09 1.26E-09 J.3AC.10 40 DATA NO DATA NO DATA 9.25E 05 LA142 1 28E.10 5.82E.11 1.45E-11 NO DATA NC OATA 40 DATA 4.25E.07 CE141 9.36E-09 6.33E-09 F. l et.10 NO DATA 2 94E 09 NO DATA 2.42E 05 CE143 1 65E-09 1.22E-06 1.35E.10 NO DATA 5.37E.10 NO D AT A 4.56E.05 CE144 4.R8E-01 2.04E-07 2.62E 08 NO DATA 1.21E-07 NO DATA 1.65E-04 PR143 9.20E-09 3.69E-09 4.56E-10 40 OATA 2.13E-09 NO DATA 4.03E-05 ... ~ ...................................................................4.33E-18 PRl44 3 01E-11 1.25E.11 1.5 st-12 40 OATA 7.05E.12 NO DATA N0147 6.29E-09 7.27E-09 4.35E-10 NO DATA 4.25E-09 40 DATA 3.49E 05 h 19F 1.03E.07 8.61E.08 3.01E 0 8 40 DATA NO DATA NO DATA 2.82E.05 c ..~........_............................ ~.... .................2.40E-05 NP239 1 1%E-09 1.11C-10 6.45E-11 NO DATA 3.65E-10 NO DATA } i i I 2.0.8 0D04, Ferini-2 2673W/0051W, 05/24/84 "*"~8' ""'""N

• • =-<w,%.,

TABLE 2.2-9 EXTERNAL DOSE FACTORS FOR STANDING ON CONTAMINATED GROUND

• 2 (mrem /hr per pel/m )

ELEMENT TOTAL BODY SKIN H-3 0.0 0.0 C-14 0.0 0.0 NA-24 2.5 1-08 2.90E-08 P-32 0.0 0.0 Cr-51 2.20E-10 2.60E-10 Mn-54 5.80E-09 6.80E-09 Mn-56 1.10E-08 1.30E-08 Fe-55 0.0 0.0 Fe-59 8.00E-09 9.40E-09 Co-58 7.00E-09 8.20E-09 Co-60 1.7T-08 2.00E-08 Ni-63 0.0 0.0 Ni-65 3.70E-09 4.30E-09 Cu-64

1. 50E-09 1.70E-09 Zn-65 4.00E-09 4.60E-09 Zn-69 0.0 0.0 Br-83 6.40E-11 9.30E-11 Br-84 1.20E-08 1.40E-08 Br-85 0.0 0.0 Rb-86 6.30E-10 7.20E-10 RD-88 3.5T-09 4.0 C 09 Rb-89

1. 50E-08

c0E-08 Sr-89 5.60E-13 6.50E-13 Sr-91 7.10E-09 8.30E-09 Sr-92 9.00E-09 1.00E-08 Y-90 2.20E-12 2.60E-12 Y-91M 3.80E-09 4.40E-09 Y-91 2.40E-11 2.7 T-11 Y-92 1.60E-09 1.90E-09 Y-93 5.70E-10 7.80E-10 Zr-95 5.0 1 -09 5.80E-09 Zr-97 5.50E-09 6.40E-09 Nb-95 5.10E-09 6.00E-09 Mo-99 1.91-09 2.20E-09 Tc-99M 9.60E-10 1.10E-09 Tc-101 2.70E-09 3.00E-09 Ru-103 3.60E-09 4.20E-09 Ru-105 4.50E-09 5.10E-09 Ru-106 1.50E-09 1.80E-09 Ag-110M 1.80E-08 2.10E-08 Te-125M 3.50E-11 4.80E-11 Te-127H 1.10E-12 1.30E-12 Te-127 1.00E-11 1.10E-11 Te-129M 7.70E-10 9.00E-10 Te-129 7.10E-10 8.40E-10

• Reference 3, Table E-6 i

00CH, Femi-2 2.0-49 2673W/0051W, 05/24/84

TABLE 2.2-9 (Continued) ELEMENT TOTAL BODY SKIN Te-131M 8.40E-09 9.90E-09 Te-131 2.20E-09 2.60E-06 Te-132 1.70E-09 2.00E-09 I-130 1.40E-08 1.70E-08 I,-131 2.80E-09 3.40E-09 I-132 1.70E-08 2.00E-08 I-133 3.70E-09 4.50E-09 I-134 1.60E-08 - 1.90E-08 I-135 1.20E-08 1.40E-08 Cs-134 1.20E-08 1.40E-08 Cs-136

1. 50E-08 1.70E-08 Cs-137 4.20E-09 4.90E-09 Cs-138 2.10E-08 2.40E-08 Ba-139

-2.40E np 2.70E-09 Ba-140 2.10E-09 2.40E-09 Ba-141 4.30E-09 4.90E-09 Ba-142 7.90E-09 9.00E-09 La-140 1.50E-08 1.70E-08 La-142 1.50E-08 1.80E-08 Ce-141 5.50E-10 6.20E-10 Ce-143 2.20E-09 2.50E-09 Ce-144 3.20E-10 3.70E-10 Pr-143 0.0 0.0 Pr-144 2.00E-10 2.30E-10 Nd-147 1.00E-09 1.20E-09 W-187 3.10E-09 3.60E-09 Np-239

9. 50E-10 1.10E-09 0004, Femi-2 2.0-50 2673W/0051W, 05/24/84 I

^ l TABLE 2.2-10 INDIVIOUAL USAGE FACTORS

• IWANT CHILO TEENAGER AOULT Milk Consumption Rate, '

330 330 400 310 Sp-(liters / year) Meat Consumbhon Rate, 0 41 65 110 U,p (kg/ year) Fresh Leafy Vegetation Consumption Rate, Ud (kg/ year)- 0 26 42 64 Stored Vegetation ConstJnption Rate, Ss(kg/ year) 0 520 630 520 Brgathing Rate (nP/ year) 1400 3700 8000 8000 ' Reference 3, Table E-5. i 1 ODN, Femi-2 2.0-51 ] 3 2673W/0051W, 05/24/84 l

TABLE 2.2-11 STABLE ELEMENT TRANSFER OATA* MILK Ff - MEAT m -(COW) Fm(- MILK ELEMENT F GOAT) H 1.0E-02 1.7E-01 1.2E-02 1.2E-02 1.0E-01 3.1E-02 C 4.E-02 4.0E-02 3.0E-02 Na P 2.5E-02 2.5E-01 4.6E-02 Cr 2.2E-03 2.2E-03 2.4E-03 Mn 2.5E-04 2.5E-04 8.0E-04 Fe 1.2E-03 1.3E-04 4.0E-02 Co 1.0E-03 1.0E-03 1.3E-02 Ni 6.7E-03 6.7E-03 5.3E-02 Cu 1.4E-02 1.3E-02 8.0E-03 Zn 3.9E-02 3.9E-02 3.0E-02 Rb 3.0E-02 3.0E-02 3.1E-02 Sr 8.0E-04 1.4E-02 6.0E-04 Y 1.0E-05 1.0E-05 4.6E-03 Zr 5.0E-06 5.0E-06 3.4E-02 Nb 2.5E-03 2.5E-03 2.8E-01 Mo 7.5E-03 7.5E-03 8.0E-03 Tc 2.5E-02 2.5E-02 4.0E-01 Ru 1.0E-06 1.N-06 4.0E-01 Rh 1.0E-02 1.0E-02 1.5E-03 Ag 5.0E-02 5.0E-02 1.7E-02 Te 1.0E-03 1.0E-03 7.7E-02 I 6.0E-03 6.0E-02 2.9E-03 Cs 1.2E-02 3.0E-02 4.0E-03 Ba 4.0E-04 4.0E-04 3.2E-03 La 5.0E-06 5.0E-06 2.0E-04 Ce 1.0E-04 1.0E-04 1.2E-03 Pr 5.0E-06 5.0E-06 4.7E-03 Nd 5.0E-06 5.0E-06 3.3E-03 W 5.0E-04 5.0E-04 1.3E-03 Np 5.0E-06 5.0E-06 2.0E-04 ' References 3, Table E-1. l i, 0004, Fermi-2 2.0-52 l 2673W/0051W, 05/24/84 l

- 2.3 MTEOROLOGICAL MODEL - 2.3.1 ATMOSPERIC DISPERSION Atmospheric. dispersion for releases is calculated using a mixed < node form of the straight line flow Gaussian model. s X/Q = average atmospheric dispersion (sec/m') for a given wind fection (sector) and distance. di -1 [ = 2.03 6 K h E , (1-E) exp (-1/2 (h/oj) ) ujkj UjkDj Nr E 1 2.03 = (2h )l/2 divided 5y the width in radians of a 22.58 sector i (0.3927 radians). 1 = number of hours meteorological conditions are observed to be in a n jk given wind direction, windspeed class k, and atmospheric stability classJ. d NOTE: If periodic data (hourly) are used instead of the joint frequency data, all variable subscripts are dropped, the nj,k is set equal to 1 and the hourly averaged meteorological variables are entered 4 into the model. y I = total hours of valid meteorological data throughout the period of N I effluent release. i = distance from the release point to location of intferest (meters) r = wind speed (midpoint of windspeed class k) measured at the 10 meter l ujk i level (m/sec) during atmospheric stability class j 1 i U = wind speed extrapolated to the effective release height using the p wind power law with the site-specific wind power law exponent. I i 0004, Femi-2 2.0-53 l 2673W/0051W, 05/24/84 I ..... _ -- __,~,

o b /2n)12 (a)2 2 Ij = the lesser of or where (/3 oj) = vertical standard deviation of the pime (meters) at distance r for oj 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. Normally 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 = maxim m height of adjacent building either upwind or downwind from the release point. AT = vertical temperature gradient (*C/100m). E = fraction considered as ground level releases y 1.0 for _P.1 1.0 u 2.58 - 1.58 ( 0 ) for 1.0 < b 1.5 i u u E = - 0.06 (b for 1.5 < b 5.0 i 0.3 u u W 0 for ._9.> 5.0 u ~ ODCN, Fermi-2 2.0-54 2673W/0051W, 05/24/84 1

O

o. vertical cxit velocity from the vent.

g u = horizontal wind speed at the point of release. i h = effective height of release (m) 1 h = 4 + hr - c, =5'ightofreleasepoint hy ] hr = additional height due to plume rise (m): for neutral or unstable conditions &T < -0.5 *C/100m) ~ 2/3 1/3 1.44 (wOi (D-d u d 4 l hr = the lesser of or 3 d u } for stable conditions GT > -0.5 *C/100n): F' 1/4 4 L!!!) i S or i 1.5 (F' ) 1/3S -1/6 I hpr = the lesser of m u 4 I or ' 4r for neutral or unstable conditions (in t the event that tbr for neutral or unstable i conditions is less than h for stable pr conditions) J d = diameter of plant vent l = correction for low vent exit velocity (m) l c, ) l 00CN, Femi-2 2.0-55 2673W/0051W, 05/24/84 i

W -W 3(1.5 - 01 d for 9 < 1.5 -~ u u c = y for b > 1.5 0 u 2 momentum flux parameter (m# sec ) / F,' = F,'; m.. (W,)2 (d/2)2 S = restoring acceleration per unit displacement -4 ~ 8.75 x 10 sec for -0.5 < A T < 1.5 -3 -2 1.75 x 10 sec for

1. 5 < A T < 4. 0 S

= 2.45 x 10-3 -2 sec for AT > 4.0 2.3.2 RELATIVE DEPOSITION Relative deposition per unit area is calculated for a mixed-mode release. (m-2), for a given wind D/Q = relative deposition per unit area direction and at a given distance. i ~ = 2.55K [(E) ( g ) + (1 - E) D ], where r e t i D = relative deposition mode for the ground-level portion of mixed-mode g releases from Figure 2.3-6. D, = relative deposition rate for the elevated portion of mixed-mode releases obtained from one of Figures 2.3-7 through 2.3-9. 2.55 = [ radians per 22.58 Sector]-1 1 i l l ODO4, Fermi-2 2.0-56 i 2673W/0051W, 05/24/84 l

i g8 SITE (DISTANCE-0.Okm 1.2 km }.6km 2.4km 3.2km 4.Okm 4.8km 5.6km 6.4km 7.2km 8.0km I BOUNDARY METERS) 0.5mi 0.75mi s.0ml 1.5mi 2 mi 2.5mt 3.0mi 3.5m1 4.9mf 4.5m1 5.0mi l g2 M 1.13 (1249) 1.11 k.13 1.14 1.15 1.18 1.18 1.20 1.14 1.08 1.06 1.04 $T k.34 1.40 1.39 1.35 1.32 1.29 1.26-Ed MNE 1.32 (1646) 1.23 1.27 1.32 1.35 R 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 o" 5 1.57 (1417) 1.39 1.51 1.62 1.67 I.60 1.69 1.65 1.60 1.51 1.39 1.32 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 f.57 1.53-1.46 l

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 J 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 wW 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 f w MW 1.18 (915) 1.16 1.22 1.27 1.29 1.26 1.40 1.44 1.41 1.34 1.27 1.26-l MMW 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 j Linear interpolation within a sector at distances lying between those shwon in the table is l l given by: [F'F\\ [F Rg2~IN21 2 l 1 4

• ("24) k "2 ~ "I )

~* 1 & R ) specified in the table, Where R, is that distance lying betwcen the distances (R 4 2 l '*I"8 ' SE'* ""C Fg &.F2'" l i \\ I i TM3LE 2.3-1 Open Terrain Recirculation Factor

FIGLRE 2.3-1 ~ V;rtical Standard Deviation of Matorial in a Plume (0 )O 7 (Letters denote Pasquill Stability Class) 1000 s I r s 1 i I / J' / / / / / / m / / f ) { j j f / / / / / / [ / j y A l A J J 100 / / s' / / a / / / / / / f f J' j j s a / / / / l ! /c / / f g ff y E / / / o E /// /?/ / / / / /,/ y ) / G go 5 / / / / / / / 7 / / / i I / / / / / I / / 1 / / i ,I 0.1 1.0 10 100 2 1 PLUME TRAVEL DISTANCE (KILOMETERS) I i I Temoerature Channe Pasquill Stability I withHeinht(i)(OK/100m) Catenories Classification A Extremely unstable <-1.9 -1.9 to -1.7 8 Moderately unstable -1.7 to -1.5 C Slightly unstable -1.5 to -0.5 0 Neutral

• Reference 6

-0.5 to 1.5 E Slightly stable 1.5 to 4.0 F Mnderately stable I > d.0 G Extremely stable l ~ 0D04, Femi-2 2.0-58 i 2673W/0051W, 05/24/84 l i . - -. -. - - -.. - - -. -,.. -.. ~. -., -. - -. - -. -. - -..... -. - -.

F1GLRE 2.>2 Plun2 Depisti:n Effset for Ground-Level Relcas2s' (All Atmospheric Stability Cicsz:s) q E o 2 s g i ) I F / t_ / / l U / k r _x 5-M M' E8 i o l '5 Y E $d / Eaw!' l / E / 4,E l Ci 5g / .J G ws ki a8 e2 w e b5 is l oa 1 l I h I l I .g I g I g E I l l e-d q m' M N M w M N e o e o o o o o o d I

• Reference 6 3Wnld NI DNINIVWEW NOlj.3VWd 2.0-59 ODCN, Fenni-2 2673W/0051W, 05/24/84 j

l FIGURE 2.3-3 w Pltaa Cepicticn Effget for 30-a Reiscsas l ( (Letters denote Pasquill Stability Class) o* [ f f z r 1 8 1 / / e f / / fff f f i /// Y / /,/= I.. a n. i {U E $g a = _f-G. ~ E r 2 e5I 1 i r C I D Te l II f o G 11 // g a 3 E // 3 4 i B ri 5 = z ff n Q l 5 E g I 5 w W E

e. e :,

I i JJ 1 il i i IT E i f i 4 1 1 i i I i ,d o. o. m. W. A w c'l N. o e o e o e o o o oRefereme 6 EWnld Ni DNINfYWIU NOll3WWd 00CN, Fermi-2 2.O 2673W/0051W, 05/24/84

FIGlRE 2.3 4 Plum 2 Depiction Effcct for 60-m Relcas2s (Letters d: note Pasquill Stability Class) l 2~6 / O. A ) 8 i s a I f I T f f v / / 3 / / i / / d e/ / I, ~ -- m m 'g .g g { w -2 4 q-m a. Um Es, sa h / oEes l g C II VI y Al z l / / /'7 E 4 o x ]l s 5 3 I B m I t-O w E E c 3 h D 2 1 f a I I ( l e.o 8 m. at e: e. att g n N e o e o e o o e o o EWold NI ONINIYW3W NOll3VWA

• Reference 6 0D04, Fermi-2 2.0-61 2673W/0051W,' 05/24/84

FIGLRE 2.3-5 Pitme DeplGtien Effact far 100 e Reitses (Letters denote Pasquill Stability Class) ) / J o.g 1 1 I s e J / / / f f / / y } i = E .a N Is. !8 J l "w w gg i z ,A =< R. l 1 1 E I I q d e w f l e E I l f // I i {* f/ I E S E- ~5 g w> l eM s e w b~~2 g 8 ~8 9 t l g mE D E5 4 4 3 w f q f e= i I i J i i l i j t i e.o ( 9 9 4 5 o M M N 9 e e o o e o o o e o i l

• Reference 6 EWMd NI DNINIVW3W NOllDYWd i

DDCM, Fermi-2

2. 462 2673W/0051W, 05/24/84

,,,,.--,,---.,.-,-,._-,.,-.n.. _,_._,---.n.,._,,.,_,.--_..v__,__ .__w,.,wn,._.,_m,__,,

FIGlRE 2.F6 Relative Deposition for Ground-Level Releases * (All Atmospheric Stability Classes) 4 10 Y i 104 \\ 3 E \\ h i t \\ E T z h \\ p N E N z g %( I l 10-5 \\ F s. N 4 E s's i y N E N t \\ i E 10-6 i i i I l 10-7 0.1 1.0 10.0 100.0 200.0 I PLUME TRAVEL DISTANCE (KILOMETERS) I Relative Deposition for Ground Level Releases (All Atmospheric Stability Classes) Reference 6 ODN, Fermi-2 2673w/co31W, 05/24/84 2.0-63

.. ~ FIGLRE 2.3-7 o i Re

• e Deposition for 30an Relessas (Letters denote Pasquill Stability Class)

= UNSTABLE (A,B,C) 104 s"( / \\ 3 gw I x T \\ 3 7 h g g [ \\\\ NEUTRAL e / NN a r s qs "'UTRAL (D) g 5 4 k STABLE p 10 l / f m i y x I 7x x Y \\ A w Q / / X'%\\ w 4 'a 2 / ( T % i e- !~ / / N w N S STABLE (E,F,G) g4 5 } N I g l I r I i. . I / I / l 10-7 0.1 1.0 10.0 100.0 200.0 PLUME TRAVEL DISTANCE (KILOMETERS) t i Relative Deposition for 30e Releases (Letters denote Pasquilt Stability Dess) o Reference 6 2.0-64 0D04, Femi-2 2673W/0051W, 05/24/84 . ~ -. -..-.,...~.-_m..-.-.- .....,..----,---.-~.----*.m,. .r---.-...-.---. _--m-,-..-i

FIGURE 2.3-8 ~ Relative Deposition for 60-m Releases (Letters denote Pasquill Stability Class) 1d f m UNSTABL E (A.8,C) [ \\- / N f / N 8 ggy6 ) NEUTRAL (D) l l 1 x gw / I W / / NA E / \\ ^ UNSTABLE / \\ '%Ql E NEUTRAL i x x l1(P4 G E / g I g s / / I } w g 5 I l E 177 i STABLE (E,F.G) I j 1 I I I I I I / i l 104 J O.1 1.0 10.0-100.0 200.0 PLUME TRAVEL DISTANCE (KILOMETERS) Relative Deposition for 60e Releases (Letters denote Pasquill Stability Class) j e Reference 6 1 0D04, Fermi-2 2.0-65 2673W/0051W, 05/24/84 .-.-n-n,, ,.,.e,, ,.,.n_.,,,,, ,n -,.-,,.e--,,.e,-,... ,m

p. FIGLRE 2.3-9 i Relative Deposition for 100-e Releases (Letters denote Pas @ill Stability Class) 104 i ONSTABLE (A,8,C) .,m y i N,sL t 10-5 f {' l s g i s ,x I I w f f NEUTRAL (D) yg i E / / N N i E ) / N N L l / / N N f N h i ( 5 iO4 ) \\ 1. A I B A A l I f D I A 1 1 ~a } g STABLE (E,F,G) NO DEPLETION 10-7 I 1 I 1 I i I l T ~ / I 104 1 0.1 '1A 10.0 100.0 200.0 PLUME TRAVEL DISTANCE (KILOMETERS) 4 Relative Deposition for 100e Releases (Leters denote Pasquilt Stebility Class) {

• Reference 6 t

0D04, Femi-2 2.0-66 i 2673W/0051W, 05/24/84

2.4 DEFINITIONS OF GASEOUS EFFLUENTS PARAMETERS Section of Term Definition Initial Use B = administrative allocation factor for gaseous 2.1.1 i effluent pathways. b = maximum height of the adjacent building. 2.3.1 C = monitor reading of a gaseous effluent monitor corre-2.1.1 sponding to associated sample radionuclide concentrations. D, organ dose rate at time of release (mrem /yr) 2.2.1.b = D = dose to an individual from radiciodines, trititrn, and radio-2.2.2.b nuclides in carticulate form with half-lives greater than eight days (mrem). skin dose rate at' time of release (mrem /yr) 2.2.1.a D, a D total body dose rate at time of release (mrem /yr) 2.2.1.a = D air dose due to beta emissions from noble gases (mrad) 2.2.2.a = g D = air dose due to gama emissions from noble gases (mrad) Y 2.2.2.a D/Q the sector averaged relative deposition for any distance 2.3.2 = in a given sector. W annual average relative deposition at the location 2.2.2.b = of the maximum exposed individual. 2.763 x 10-9 m-2 in the WNW sector = OD(N, Fermi-2 2.0-67 2673W/0051W, 05/24/84

Section cf Term Definition Initial Use plume depletion factor at distance r for the appro-2.3.1 6 = priate stability class (radiciodines and particulates). total body dose factor due to gamma emissions from 2.1.1 K = g; 3 r,adionuclide (mrem / year per pC1/m ) from Table 2.1-1. Skin dose factor due to beta emissions from radionuclide 2.1.1 L = y 3 i (mrem /yr per pCi/m ) from Table 2.1-1 air dose factor due to gantna emissions from radionuclide 2.1.1 t M = y 3 i (mrad /yr per pCi/m ) from Table 2.1-1. air dose factor due to beta emissions from noble gas 2.2.2.a N = g 3 radionuclide 1 (mrad /yr per pCi/m ) from Table 2.1-1. nj,.. number of hours meteorological conditions are 2.3.1 = observed to be in a given wind direction, wind-speed class k, and atmospheric stability class j. total hours of valid meteorological data. 2.3.1 N' = dose parameter for radionuclide i, (mrem /yr per 2.2.1.b P = g 3 pC1/m ) for the inhalation pathway from Table 2.2-1. rate of release of noble gas radionuclide i 2.1.1 Q = g (p C1/sec) release rate of radionuclide i for the combined source 2.1.2 Q' = g terms of routine Reactor Building Exhaust Plenum plus Containment Drywell Purge Release. cumulative release of noble gas radionuclide i over 2.2.2.s 1lk = the period of interest (pC1). l 0D04, Fermi-2 2.0-68 2673W/0051W, 05/24/84

• 4[...< f ^

^ y; c -[ Q ^ t ce K ,p-Sggion gg >.g o .c . Term , Definition e'. Initial Use \\ s n 4 pt cumulative release of radiciodin$,' tritium or 32.2.2.0f[N* "Q ' i-i r/ . material in particulate form oyeYthe* period of ' i 't \\' h interest (pC1). I f I' y> fi / N j '= ,qte of release of noble gas radiordclide 1 (pC1/sec) 2.1.3 .I 3 .Q 3 / V'* J/' from the Containment Drywell Purge. .9 3 4-dose factor for radionuclide i, (mrem /yr per pCi/m ) 2.2.2.'g 7 f,, Rg = 2 or (m -mrem /yr per pCi/sec).' y' t, 'R \\ monitor reading per mrem /yr to the skin, j. 2.1.1 = s ] ] *J * ( $A y ;* s, s i monitor reading per mrem /yr to the total t,ody. 2.1.'l A = / D = + ss '.s

• /

./ < 3000 mrem / year. ,i = ,>s ,, g1 / J , ~,l,i i '

• ,,. g tj 'c

\\ distance from the point of release / to the locatLe,m, s gj' ' 2.3.1

• )3s r

= of interest for ~ dispersion calculations (meters). i I C 5, monitor reading of the noble gas monitor at the alarm 2.1.l ' ' 2' 7 i 3 setpoint for the release pathway under considcration. i I A j verticalstandardde[iationofthehlumewith',> Y.3.1 I < = j? 3 n. v, t 3 building wake correction. s* i ?, (< vertical standard deviation of the plune (in meters), Q.5.1 oj = at distance r for ground level releases under the /o I 1 s. + 'rf ' stability category j indicated by eT, fror.> Figure 2.34 i 7 .,s is N \\'. N .(r

, J i 4

s f f 3 2.3.1 vertical l temper.ture gradient '(oC/100m,). ; N ,aT gu s'; m.,,. s. 0004, Fermi-2 2.0-69 ',?_ t c '\\ tg ' 2673W/OO51W, 05/24/84 1 ( )

• t s

( s_ ( / } .;/ _ \\c = _ J"j ;, j _ _

Section of Initial Use Term Definition terrain recirculation factor. 2.3.1 K = wind speed (midpoint of windspeed class k) at ground 2.3.1 u = jk, level (m/sec) during atmospheric stability class j. i relative dispersion for unrestricted areas at the 2.2.2.b W', = controlling receptor. the sector-averaged relative concentration at any distance 2.3.1 X/Q = 3 r in a given sector. (sec/m ) the highest annual average relative concentration in 2.1.1 X7G = any sector, at the site boundary. sec/m 4.186 x 10 sec/m in the NW sector = relative concentration for the location occupied by 2.2.2.b 77Q' = the controlling receptor. ~7 3 2.686 x 10 sec/m in the RM sector = windspeed u extrapolated to the effective release 2.3.1 U = jk height using the wind-height power law. fraction of release considered as ground-level 2.3.1 E = -2) 2.3.1 momentum flux parameter (m# sec F,' = l effective release height (m) 2.3.1 l h = l height of release point (m) 2.3.1 h = l y i l l ODO4, Fenni-2 2.0-70 2673W/0051W, 05/24/84

Section of Term Definition Initial Use aoditional height due to plune rise (m) 2.3.1 = stack exit velocity (m sec~1) 2.3.1 W, = i re, storing acceleration per unit displacement for 2.3.1 S = adiabatic motion in the atmosphere. (sec-2) horizontal wind speed at the point of release 2.3.1 u = i l l OD04, Fermi-2 2.0-71 26'i3W/0051W, 05/24/84

2.5 GASEOUS RADWASTE EFFLUENT SYSTEM AND VENTILATION EXHAUST TREATMENT SYSTEM ' Figure 2.5-1 is a schematic of the Gaseous Radwaste Effluent System showing the release points to unrestricted areas. The Ventilation Exhaust Treatment System is also presented in Figure 2.5-1. The Ventilation Exhaust Treatment System consists of EPA filters installed in the Service Building Ventilation Sys, tem and EPA and charcoal filters installed in Radwaste Building Ventilation System. ODO4, Ferini-2 2.0-72 2673W/0051W, 05/24/84

-w--- w g A4 .-we ,.-.6 m; 4 i p .h j .6 8., w g. ii 56 f(( R -3L s"o 3?.'. { {Jf{"F r W ~g ..I_ = } .M g ((t J.w. m, t-a = g y gy 7 r----- l*5~ = n. L .r- (({ ,,,, m."~ 4 p ,,,,, t =," l " ,o i it .... i } 5 '= 8 s

T

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3: w l 1 I is ~ .nw, 4 o .n.1, w a a isi R V i. p !!!1lll::t ll R. m ~ h - e g._ p ,W, s = I \\ l m e. b V no s.e-l , u.c m. m m. GASEOUS RADWASTE EFFLUENT SYSTEM j wi.vo w,,.%,,, i 4 i

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

TABLE 3.0-1 ENVIRONENTAL RADIOLOGICAL MONITORING PROGRAM (Samplin0 Locatims) Station Distance fran Nunber Direcion Reactor (Approx) Descript1on Media Frequency 1 NE 1.3 mi, Estral Beach (ccanmity) Direct Radiation Q Pole on Lakeshore,18 Radiciodine W Poles S. of Lakeview Particulates W 2 WE 1.1 mi. Tree at the termination Direct Radiation Q Brancho Street (private residence) 3 N 1.1 mi. Pole at NW corner of Direct Radiaticn Q Swan Boat C1Lb Fence (Ccmnunity) 4 NNW 0.6 mi. Site Bomdary and Toll Direct Radiation Q Road, on Site Fence by Radiciociine W APS #4 5 NW 0.6 mi. Site Bomdary and Toll Direct Radiation Q Road on Site Fence by Radioicdine W APS #5 Particulates W 6 WNW 0.6 mi. Pole NE corner of bridge Direct Radiation Q over Toll Road 7 W 15 mi. Pole, behind Doty Farm, Direct Radiation Q 7512 N. Custer Road Radiciodine W (control) Particulates W Milk M S-1 NW 2.4 mi. Pole NE corner Dixie Direct Rediation Q Highway and Post Road S-2 ff4W 2.4 mi. Pole NW corner Trombley Direct Radiation Q Road and Swan View Road S-3 N 2.6 mi. Pole on S side Massarant Direct Radiation Q ~ - 2 Poles W of Cinavarre S-4 WE 6.5 mi. Pointe Mouillee - W. Direct Radit. tion Q Jefferson and Canpau Road, l Pole on SE corner of Bridge l S-5 E 5.1 mi. Pointe Mouillee Game Area Direct Radiaticn Q - Field Office, Pole near tree north area of parking lot ODCM, Ferini-2 3.D-2 2767W/0051W, 05/24/84 . ~ - ~..

TABLE 3.0-1 ENVIRONENTAL RADIOLDGICAL MONITORING PROGRAM (CONTINUED) Station Distance fran Nunber Direcion Reactor (Approx) Descripticri Media Frequency S-6 N 4.5 mi. Labo and Dixie Highway - Direct Radiation Q Pole on Sw corner with light S-7 PNW 5.0 mi. Labo and Brandon - Pole Direct Radiation Q on SE corner near RR S-8 NW 4.0 mi. Pole NW corner Newport Direct Radiation Q ano Brandon Roads S-9 WNW 4.9 mi. Pole on SE of War and Direct Radiation Q Post Roads S-10 W 5.5 mi. Pole on NE corner Nadeau Direct Radiation Q and Laprad near mobile i home park S-Il SW 4.5 mi. Pole on NW corn 5r Mentel Direct Radiation Q and Hird S-12 SW 4.9 mi. Pole in parking lot of Direct Radiation' Q Department Natural Re-sources Office Building - Sterling State Park S-13 W 2.8 mi. Pole S side Williams Rd. Direct Radiation Q - 8 Poles W of Dixie Hwy. (Special Area) S-14 WSW 2.8 mi. Pole N side of Pearl at Direct Radiaticri Q Parkview - Woodland Sch. (pcpulated area) S-15 S 0.9 mi. Pole N side of Point Aux Direct Radiation Z Peaux 2 Poles W of Long (site bomdary) S-16 SSW 1.0 mi. Pole S side of Point Aux Direct Radiation Q Peaux - 1 Pole W of Huron next to vent pipe (site bomdary) S-17 SW 0.9 mi. Fermi gate along Point Direct Radiaticri Q Aux, Peaux Road - cri fence post W of gate (site bomdary) l l 3.0-3 CDCM, Fermi-2 2767W/0051W 05/24/84 j 3

-TABLE 3.D-1 4 ENVIRONENTAL RADIOLOGICAL MONITORING PROGRAM (CONTINUED) Station Distance from Nunber Direcian Reactor (Approx) Description Media . Frequency S-18 WSW mi 1.2 mi. Pole on Toll Road - 13 Direct Radiation Q Poles S of Fermi Drive 5-19 W 1.0 mi. Pole on Toll Rd., 6 Direct Radiation Q Pales S of Fermi Drive S-20 SSW-6.2 mi. Pole NE corner McMillan Direct Radiation Q and East Front Street (Special Area) S-21 SW 10.1 mi. Pole SE corner of Mortar Direct Radiation Q Creek and Laplaisance S-22 SWS 9.9 mi. Pole E side of S. Dixie Direct Radiation Q 1 Pole S of Albain S-23 WSW 8.0 mi. Pole Cluster (St. Mary's) Direct Radiation Q Park corner of N Custer and Dixie (Monroe St.) (N side, next to river) (Special Area) S-24 WSW 9.2 mi. Pcle Milton " Pat" Mtnson Direct Radiation Q Recreational Reserve - N Custer Road (Control) S-25 WNW 10.1 mi. Pole corner Stony Creek Direct Radiation Q and Finzel Roads S-26 NW 8.7 mi. Pole W side Grafton Road Direct Radiation Q 1 Pole N of Ash /Grafton intersection S-27 NNW 9.9 mi. Pole E side of Port Direct Radiation Q Creek,1 Pole S of Will-Carlton Road S-28 N 6.9 mi. Pole on S side of S. Direct Radiation Q Huron River Dr. across fran Pace Street (Special Area) S-29 N 9.5 mi. Pole NE corner of Direct Radiation Q Gibraltar and Cahill Roads 3.0-4 ODCM, Fermi-2 2767W/0051W, 05/24/84

TABLE 3.0-1 ENVIRONENTAL RADIOLOGICAL MONITORING PROGRAM (CONTIl0ED) Station Distance from Nunbar Direcicri Reactor (Approxi Description Media Frequency S-30 PNE 9.9 mi. Pole S corner of Adams pirectRadiation Q and Gibraltar (across from Hunbug Marina) 8 5 0.9 mi. Point Aux Peaux, Sediment SA 100-300 ft. offshare sighting directly to land based water tower 9 E 0.2 mi. Fermi-2 discharge, Sediment SA approx. 200 f t. offshore 10 NE 1.1 mi. Estral Beach, approx. Sediment SA 200 ft. offshore sighting directly to land based windmill 11 'NNE 9.5 mi. Control in vicinity of Fish SA Celeron Island 12 SSE 0.4 mi. Fermi Unit I Raw Lake Surface Tater M Water Intake Structure 13 S 1.2 mi. Monroe Water Station Drinking Water M N side of Pointe Aux Peaux 1/2 block W of Long Rd. 14 NE 13 mi. DECO's Trenton Channel Surface Water M Power Plant Intake Structure (Screenhouse #2) 15 tee 20 mi. Detroit (Allen Park) Drinking Water M Water Station 14700 Moran Rd. 16 E 0.4 mi. Fermi-2 discharge Fish SA (approx.1200 f t. offshore) 17 SW 1.0 mi. Corner of Erie St. and Radiciadine W~ Point Aux Peaux Rds. Particulates W 18 WSW 2.0 mi. L. Burns Farm Milk M-SM l 4352 Pointe Aux Peaux 20 NW 5.7 mi. Reaune Farm Milk M-SM 2705 East Labo 3.0-5 CDCM, Fermi-2 2767W/0051W, 05/24/84 l l

TABLE 3.0-1 0 ENVIRONENTAL RADIOLOGICAL MONITORING PROGRAM (CONTINUED) Station Distance fran Nunber Direcion Reactor (Approx) Descripticn Media Frequency i 22 W 0.6 mi. Outlet Fermi-2 Storm Sediment SA Drains 31 NW 4.5 mi. Yoas Farm Milk M-SM 3239 Newport Rd.

• C 32 NNE 4.0 mi.

Roland Farm Milk M-SM 9501 Turnpike Hwy. 1 t W1 S 0.4 mi. Approx.100 f t. W of Grotrk: water On Lake Erie, 5 end of flow f crmer plant citbhouse reversal site W2 SSW l.0 mi. 4 f t. S of Pointe Aux Grotndwater On Peaux (PAP) Rd. fence, flow 427 ft. W of where PAP reversal crosses over Stoney Point's western dike W3 SW l.0 mi. 143 ft. W of PAP Rd. Grotndwater On gate, 62 f t. N of PAP flow Rd. fence reversal W4 WNW 0.6 mi. 42 ft. N of Langton Rd., Grotndwater On 8 ft., E of Toll Rd. flow fence reversal l l l 1 ) i l l ODCM, Fermi-2 3.0-6 2767W/0051W, 05/24/84

TABLE 3.0-1 ENVIRONENTAL RADIOLOGICAL MONITORING PROGRAM (CONTINUED) Station Distance fran Media Frequency Nunber Direcion Reactor (Approx) Description Sediment SA 22 W 0.6 mi. Outlet Fenni-2 Storm Drains M-SM I Milk 31 NW 4.5 mi. Yoas Farm 3239 Newport Rd. Milk M-SM 32 NNE 4.0 mi. Roland Farm 9501 Turnpike Hwy. On Gromdwater W1 S 0.4 mi. Approx.100 f t. W of flow Lake Erie, S end of reversa3 former plant citbhouse site W2 SSW 1.0 mi.- 4 ft. S of Pointe Aux Gromdwater On flow Peam (PAP) Rd. fence, reversal 427 ft. W of where PAP crosses over Stoney Point's western dike On W3 SW 1.0 mi. 143 f t. W of PAP Rd. Gromdwater flow gate, 62 f t. N of PAP reversa Rd. fence W4 WNW 0.6 mi. 42 f t. N of Langton Rd., Gromdwater On flow 8 ft., E of Toll Rd. revers: fence 3.0-6 00CM, Fermi-2 2767W/0051W, 05/24/84

FIGURE 3.0-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM - SAMPLIN' LOCATIONS BY STATION NUMBER (IMEDIATE AREA) ~ l. N~ / \\.n, / h .\\ c k ]- js.,( s)' SWAN s CREEK 10 Y S g, e- ~ .s I ~~ % ft a y '"1 S-l SCALE OF MILE [l 0 I S-1 y -15 ,,,, # w3i-ir #2 I LAKE LEGEND 18 hAhkh ohl h Y NARTICULATES

• ig,#

S-1 ERIE g $oh!Ux$UEOST!kEE"ICEWATER s 4 a r-75-i4 \\ rIcuRE i j SAMPLING LOCATIONS l BY STATION NUMBER (SITE AREA)

FIGURE 3.0-2 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM - SAMPLING LOCATIONS BY STATION NUMBER (GREATER THAN 5 MILES) ~ } f

• "~~ A L JM I

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n 432iO 4 8 ~ S, LEGEND y ig / _r, ens l. b. e DIRECT RADIATION s ERIE b i. g,' ' O RADIOIODINE OR PARTICULATES $OR K WTRS ACE WATER / a cRe'JND WATER UICHIGA_N; j. j ML.YE / D WILK OHIO BA* l *co FIGURE 2 ,N . ROE 45)#{Es, ,x g A l

FIGURE 3o0-3 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM o SUPPLEMENTARY TLD LOCATIONS - BY STATION NUMBER H 1.m. mn.,R 4 A i N

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's LEGEND LAKE N S2 %\\ e DIRECT RADIATION s-2 ERIE 'N O RADIOIODINE OR PARTICULATES A FISN AN0/OR SEDIMENT 1 A DRINKING WATER / SURFACE WATEH f 4,,, S-21{ E GROUND WATER 4 g D MILK r--- J-FIGURE 3 --m l [*g'--~~ ]8 SAMPLING LOCATIONS K l H ll 34?' NOTE ll sy siATION NUMBER !!FORSITEAREA. SEE FIC 1 FOR GREATER THAN 5 MILES. as SEE FIC.2 l lj FOR LESS INAN 10 MILES. SEE FIG.3. l _-j y 6

3.2 INTERLABORATORY COH'ARISON PROGRAM DESCRIPTION l The RDF Contractor is required to participate in a Commission approved Interlaboratory Comparison Program and to stbmit QA Program Progress sunmary reports to DECO on a bi-4nonthly or quarterly basis. These reports contain sunmary descriptions and performance data sunmaries on reference standards, kank, blind, spiked, and dtplicate analyses as well as the USEPA and other i Iporatarf ~.Interemparison Programs, as applicable. A sunmary of the Interlaboratory Conparison Program results obtained is required to be included in the Annual Radiological Environmental Operating Report pursuant to Specification 6.9.1.7. Participation in an approved Interlaboratory Comparison Program ensures that an independent check on the precision and accuracy of the measurements of rsdioactive material in environmental sample matrices is perf armed. as part of the QA program for environmental monitoring in order to demonstrate that the results are valid for the purpose of Section IV. B.2 of Appendix I to 10 CFR Part 50. 00CM, Fermi-2 3.0-10 2767W/0051W, 05/24/84

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

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'5,* -Q .,A [ [ .r.._,N ( ' k g.g Y l \\ qV y ! *\\ i4 $l 'I f 2 1 I. esse. y I J7 Ea558. g g g gdig [. h[,,/.cf sj hilpl 'g ll N. f. nLf 3 's w't t.. 1 . v, s w*.; x s . j,e e 1 00CM, Fermi-2 4.0-2 3171W/0051W, 07/23/84 k __ -}}