Text

Changes to Offsite Dose Calculation Manual.
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Issue date:	08/28/1987
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ENCLOSURE 3 TENNESSEE VALLEY AUTHORITY BROWNS FERRY NUCLEAR PLANT CHANGES TO THE OFFSITE DOSE CALCULATION MANUAL t 870903038i 870828 PDR ADOCi( 05000259 PDR

ODCH Chan es This report is to comply with Technical Specifications Section 6.10 reporting requirement'or changes to the ODCH. The original ODCH was submitted in 1983 and has been revised extensively. The Radiological Effluent Technical Specifications (RETS) were implemented at BFN on Hay 6, 1987. Therefore, this is our first report of ODCH changes and includes all the changes since 1983.

Because of the large number of changes, a copy of the entire current ODCH is included with this report.

Descri tion of chan es The revised Section 1.0 (Gaseous Effluents) of the Browns Ferry Nuclear

~

Plant (BFN) Offsite Dose Calculation Hanual (ODCH) is attached.

~

A summary of the major changes (those involving the dose calculational methodology) is as

~ ~

fo1 1 ows:

1. Heteorological data period of record revised from 1974-75 to 1977-79.

2. Split-level JFD not considered for release rate limits.

3. Wind speed midpoint for > 10.9 m/s revised.

4. Instantaneous release rate limits revised due to new meteorological data and new finite cloud approximation.

5. Finite cloud approximation revised for stack releases.

6. Critical receptor locations revised to agree with latest land-use census data.

7. Nuclides analyzed on a monthly basis were expanded for noble gases and iodines and particulates.

8. Heteorology for dose projections has been included.

Anal sis or Evaluation Justif in 'the Chan e These changes are made to reflect changes in methodology which have been implemented at other TVA plants in the time since the BFN ODCH was originally submitted to NRC in 1983. These changes are an attempt to make the BFN ODCH consistent with other plants and with the current models being used for dose assessment in TVA.

the Set pints or Dose Calculations These changes will cause the setpoint calculations and dose calculations to be more reliable and more accurate due to the improvements in the model.

Desc i tion of chan~ c Section 2,0 (Liquid Ef fluents) was rewritten to clarify the descriptions of the calculations being performed. The majority of the changes were not changes in methodology; rather, they involved the movement of paragraphs, the addition and/or deletion of text to make the description clearer to the reader, and the changing of subscript identifiers in order to use the same subscripts for the same quantity throughout the section. These minor editorial changes require no analysi or justification and will not change the setpoints or dose calculations.

The major changes involving the dose calculational methodology being used are outlined below:

Section 2.3.3 Honthly Analysis

1. The l: st of isotopes considered was expanded to include 18 single isotopes and two parent/daughter pairs in the calculation.

2. 'The list of or'gans considered in the calculation was expanded.

Organs considered are the bone, gastrointestinal tract, thyroid, liver, and total body.

3. The child age group was added to the adult age group for consideration.

4. The volume of water used:for dilution in the calculation was changed from the .dilution flow during releases to the average riverflow past the site for the month.

5. A recreational dose is calculated for the monthly analysis which considers 4 isotopes (Co-58, Co-60, Cs-134 and Cs-137) which are expected to contribute over 95'/. of the total recreational dose.

The total body dose due to shoreline exposure is calculated for .-

these 4 nuclides and added to both the total body and.the maximum organ doses.

6. The administrative (guideline) release limits, given in curies, were deleted.

7. Several sentences were added to section 2.3.2.4 to outline how the final monthly doses are obtained, i.e., how the individual pathway. doses are summed to find the total body "nd maximum organ doses to be compared to the Technical Specif ications.

Descript on of chan.es (continued)

Section 2.3.3 Quarterly and Annual Analysis The recreation pathway was added to the quarterly and annual analysis section.

The skin was added as an organ to be considered in the analysis.

3. The child age group was added to the calculation.

4 ~ The consumption rates were made consi tent by taking all values from Regulatory Guide 1.109.

5. A calculation of population doses was added.

6. The section containin activity 'mits for releases was dele ed.

7. Table 2.1 was replaced with an updated table reflecting the addition of nuclides to the ones already in use, and the addition of the child as an age group to be considered.

8. Tables 2.2, 2.3, and 2.4 were added to include information which is used in the calculation of doses.

Analysis or Evaluation Justifvin the Chan e These changes are made to reflect changes in methodology which have been implemented at other TVA plants in the time since the BFN ODCH was originally submitted to the HRC in 1983. These changes are an attempt to make the BFN ODCM consistent with other plants. and with the current models being used for dose assessment, in TVA.

Determination of the Effect of the Chan e on the Accuracy or reliability of the Seteoints or Dose Calculations These changes will cause the dose calculations to be more reliabl'e and more accurate due to the improvements in the model. Setpoint calculations are not affected by these changes.

Descri tion of chan es The revised Section 3.0 (Environmental Monitoring) of the Browns Ferry Nuclear Plant (BFN) Offsite Dose Calculation Manual (ODCM) is'attached. A summary of the major changes is as follows:

1. References to appropriate sections of'he Radiological Effluent Manual (REM) were included.

2. Table 3.3 (issued with the 1983 ODCM) is deleted.

3. A Table 3.3, outlining detection capabilities, is added.

Table 3.1 is revised to more accurately reflect the program including references to locations identified in the figures and tables.

5. Table 3.2 is updated to show currently identified sampling locations.

6. Figures 2.1 through 3.4 are updated.

Anal sis or Evaluation Justif in the Chan e These changes to the BFN ODCM reflect changes identified in the land-use surveys conducted for BFN. The changes are required to accurately reflect the environmental monitoring program at BFN.

Determination of the Effect of the Chan e on the Accurac or reliabilit of the Set pints or Dose Calculations These changes will have no effect on the setpoint or dose calculations.

Descri tion o-." chanrcs

~ection 4.0 is added dcscribinp the method of a su."in'hat ~0 C!'R 190 dose limits are met.

Anal si or Evaluation Just.'v.n the Chan e The. addition o. this,sect:on will doc ment in the ODOM how the total dose" .ate:.ohtained .fo- this. 40 CFR 190 evaluat=on. Tt will make =he section of. the ODCKzor.e consistent with .'he RETD roaui"cments.

I' Detarrwnation of the Effect of the Chan e on the Accuracy o-.

reliabilit of the Setooints or Dose Calculations This change will have no effect on the setpoint or dose calcula'ions.

Radiological Effluent Technical Specification (RETS) Manual Prepared By , s/s/z7 Date Reviewed By PORC Chairman a e Approved By ant ntendent ate

RETS HANUAL Section III OFFSITE DOSE CALCULATION

TABLE OF CONTENTS

~Pa e 1.1 Alarm/Tri p Setpoints 1.1.1 Release Rate Limit Methodology qCi/s Step 1 (Dose Rate)

A. Noble Gases 3 B. Iodines and Particulates 8

1. Inhalation 8

2. Ground Contamination 9

~

3. Milk Ingestion 10

4. Total Thyroid Dose Rate 13 Step 2 (Setpoints) 14 1.2 Monthly Dose Calculations 15 1.2.1 Noble Gases 16 Step 1 16 Step 2 18 1.2.2 Iodines and Particulates 20 Step 1 20 Step 2 24 1.3 l}uarterly and Annual Dose Calculations 25 1.4 Gaseous Radwaste Treatment System Operation 26 1.5.1 System Description 26 1.5.2 Dose Projections 26 2.0 Liquid Effluents 27 2.1 Release Rate Limit Methodology 27 2.1.1 RETS Requirement 27 2.1.2 Prerelease Analysis 27 2.1.3 Release Flow Rate Calculations 28

TASLE OF CONTENTS Parcae 2.2 Instrument Setpoints 29

~.l'etpoint Determination 2.2.2 Post-Release Analysis 2.3 Dose 30 2.3.1 RETS Requirement 30 2.3.2 Monthly Analysis 31 2.3.2.1 Hater Ingestion 32 2.3.2.2 Fish Ingestion 34 2.3.2.3 Recreation 35 2.3.2.4 Monthly Su+vary. 37-2.3.3 quarter)y and Annual Analysis 38 2.3.3.1 Individual Doses 38 2.3.3.2 Population Doses 41 2.4 Operability of Liquid Radwaste Equipment 2.5 Dose Projections 42 p

3'.0 Radiological Environmental Honi tor ing 43 3.1 Monitoring Program 43 3.2 Detection Capabilities 3.3 Honroutine Reports

4. Annual Maximum Individual Doses Total

LIST OF. TABLES 0"

Table Number 1.2 (Sheets 1 & 2)

Tit1e Expected Annual Routine Atmospheric Gaseous Releases from One Unit at BFN Bas i c Radi onuc 1 ice Data 1.3 (Sheets 1-22) Joint Percentage Frequencies of Mind Speed by e

Mind Direction for Stability Class 1.4 BFN Offsite Receptor Location Data 1.5 Dose Factors for Submersion in Noble Gases le6 (Sheets 1 & 2) Nuclide Specific Transfer Data 1.7 (Sheets 1 & 2) External Dose Factors for Standing on Contaminated Ground 2.1 (Sheets 1-4) Dose Commitment Factors 2.2 (Sheets 1 & 2) Fish Concentration Factors 2.3 (Sheets 1-4) Recreation Dose Factors 2.4a Public Mater Supply Information 2.4b Fish Harvest Data 2.4c Recreation Usage Data 3.1 (Sheets 1-5) Environmental Radiological Monitoring 3.2 Atmospheric and Terrestrial Monitoring Station Locations 3.3 (Sheets 1 & 2) Haximum Values for the Lower Limit of Detection (LLD)

LIST OF - FIGURES Title BFH Land Site'Boundary 1.2 BFH Offgas System and SGTS Effluent Monitoring 1.3 BFN Normal Building Yentilation

~

1.4 (Sheets 1-4) Plume Oepletion Effect (All Atmospheric Stability Classes) 1.5 Vertical Standard Deviation oS Material in a Plume (A11 Atmospheri'c Stability Classes) 1.6 (Sheets 1-4) Relative Oepositi on (All Atmospheric Stability Classes) 2.1 Assumed Liquid Effluent Restricted Area 2.2 BFH Liquid Effluent Monitors 2.3 Liquid Radwaste Treatment System Atmospheric and Terrestrial Monitoring Network 3.2 Local Monitoring Stations 3.3 TLO Locations BFN 3.4 Reservoir Monitoring Network

1.1 Gaseous Effluents 1.1 Alarm/Tri

~ Set pints Technical Specification 3.8.8.1 requires that the dose rate in

~ ~

unrestricted areas (Figure 1.1) due to gaseous effluents from the BFH site shall be limited at all times to the following values:

1. 500 mrem/yr to the total body and 3,000 mrem/yr to the skin from noble gases.

2. 1,500 mrem/yr to any organ from radioiodines and particulates.

Technical Specification 3.2.K.l requires gaseous effluent monitors to have alarm/trip setpoints to ensure that the above dose rates. are not exceeded. This section of the ODCN describes the methodology that will be used to determine these setpoints.

The methodology for determining alarm/trip setpoints is divided into two major parts. The first consists of backcalculating from a dose rate to a release rate limit relation for each nuclide type and release point. The second consists of using the release rate limit relations to determine the physical settings on the monitors. The methodology for the latter is contained in Technical Instruction 15.

1.1.1 ReIease Rate Limit Methodolo Ci/s Ste 1 Dose Rates The first step involves calculating a dose rate based on the design objective source term mix used in the licensing of the plant. Historical meteorological data are used in this calculation. Doses are determined for (1) noble gases and (2) iodines and particulates. Depending on the pathway involved, either air concentrations or ground concentrations are calculated. Figures 1.2 and 1.3 show the Offgas System, the Standby Gas Treatment System and normal building ventilation with effluent monitor 'locations.

A. Hoble Gases Equations and assumptions for calculating doses from noble gases are as follows:

Assumotions:

l. Doses to be calculated are total body and skin.

2. Exposure pathway is submersion within a cloud of noble gases.

3. Noble gas radionuclide mix is based on the expected source term given in Table 1.1.

4. Basic radionuclide data are given in Table 1.2.

5. All releases are'treated as ground level or elevated.

6. Meteorological data are expressed as joint-frequency distributions of wind speed and wind direction by atmospheric stability for the period January 1977 to December 1979 (Table 1.3). Releases fron the radwaste, reactor and turbine buildings are treated as 100 percent ground level, whereas stack releases are considered 100 percent elevated.

7. Raw meteorological data for ground level releases consist of wind speed and direct',on measurements at 10m and temperature measurements at 10m and 45m. Nindspeeds and directions for elevated releases were measured at 93m. Stability Class D was assumed to persist during the entire period for elevated releases.

8. Dose is to be evaluated at the nearest land site boundary point in each sector and at other locations expected to be maximum exposure points (Table 1.4).

9. A semi-infinite cloud model is used. The use of a finite cloud model would result in calculated doses of 0 to 10 percent higher than those calculations using the semi-infinite cloud model for BFH.

10. Ho credit is taken for shielding by residence.

ll. Plume depletion (Figure 1.4) and radioactive decay are considered consistent with Regulatory Guide 1.111 methodology.

12. Building wake effects on effluent dispersion are considered.

13. A sector-average dispersion equation is used consistent with Regulatory Guide 1.111.

14. The wind speed classes that are used are as 'follows:

Number Ran e m/s ~Hid oint

~m/s r

< 0.3 0.13 0.3-0.6 0.45 0.7-1.5 1.10 1.6-2.4 1.99 2.5-3.3 2.88 3.4-5.5 4.45 5.6-8.2 6.91 8.3-10.8 9.59 9 > 10.9 10.95 15 The stability classes used are the standard A theough G classifications. Stability classes 1-7 will correspond to A~1, 8=2, ... G=7.

t 16. Terrain To effects are not considered.

17. Environmental transfer data are consistent with NUREG/CR-1 004.

~Euati one calculate the dose from radiological effluents discharged from a given release point for any one of the 16 potential maximum-exposure points, the following equations are used.

For determining the air concentration of any radionuclide:

x; = g 9 7 g -(2/~)'

i'jt&i~ I )exp(-~i x/u;)exp(-he'/2~zk ) (1.1)

~ zk uj. (2 ex n where xj = air concentration of radionuclide i, qCi/m'.

= joint relative frequency of occurrence of winds in windspeed class j, stability class k, blowing toward this exposure point, expressed as a fraction.

Qi average release rate of radionuclide i, yCi/s.

P fraction of radionuclide remaining in plume (Figure 1.4), consistent with Regulatory Guide 1.111 methodology.

vertical dispersion coefficient, for stability class k which includes a building wake adjustment, e

zk = (~zk + 0.5A/~)

where azk = the vertical dispersion coefficient for stability class k (m) see Figure 1.5,

'0.5 a building shape factor, and A = the minimum building cross-sectional area, (2400).

uj = midpoint value of wind speed class interval j, m/s.

downwind distance, m.

number of sectors, 16.

e radioactive decay coefficient of radi onuc i de 1 i, s ~.

2~x/n = sector width at point of interest, m.

he = effective release height, m.

For effluents exhausted from release points that are higher than twice the.--

height of adjacent structures (elevated releases) the effective release .

height is determined by the following equation, consistent with Regulatory Guide 1.111 he = hs + hpr ,ht c where

= correction factor for low relative exit velocity, c = 3(1.5-Ho/u)d, where No = the vertical plume exit velocity (m/s) u = mean wind speed (m/s) and d = inside diameter of the release point, m.

hpr plume rise above release point as determined by the Briggs equations given in Sagendorf (ERL ARL-42), m hs physical height of release point, m.

ht terrain height between release'-point and I'aximum receptor location, m.

For effluents released from points less than. the height of adjacent structures, a ground level release is assumed (he 0).

For ef fluents released from points at the level of or above adjacent structures, but lower than elevated release points, releases are

.treated as follows:

Case 1 elevated if Wo/u > 5.

Case 2 ground level (he = 0) if Hp/0 < l.

Case 3 split level if 1 < wo/U < 5.

Under Case 3 a split level dispersion approach is implemented using, a model that requires for each release point two 3FDs, one for elevated releases and one for ground level releases. The summation of the elevated and ground level JFDs account for the total period of record. Releases are considered to be elevated 100(l-Et) percent of the time and ground level 100 Et percent of the time where the entrainment coefficient, Et, is defined by Et = 2.58 1.58(Wo/u) for 1 < Wo/u < 1.5 (1.1b)

Et = 0-3 0 06(Wo/u) for 1 5 < Ho/u < 5 (1.1c)

OTB = g xiOFBi (1 2) where Dla = total body dose rate, mrem/yr.

Xi = air concentration of radionuclide i, qCi/m'.

DFB; = = total body dose factor due to gamma radiation, mrem/yr per gCi/m'Table 1.5).

For determining the skin dose rate Os K xi (OFSs + 1.11 OF>i) (1.3) 1

where os skin dose rate, mrem/yr.

xi air concentration of radionuclide i, >Ci/m'.

OFSi skin dose factor due to beta radiation, mrem/yr per yCi/m* (Table 1.5).

1.11 the average ratio of tissue to air energy absorption coefficients, mrem/mrad.

DF>i = gamma-to-air dose factor for radi onuc 1 ide i, mrad/yr per qCi/m'Table 1.5).

The above dose calculations are repeated for each release point (vent or stack) and then summed to obtain maximum total body and skin dose rates. The maximum total body and skin dose rates will then=be used in step 2.

B. Iodines and Particulates Equations and assumptions for calculating doses from radiosodines and particulates are as follows;

1. Dose is to be calculated for the critical organ, thyroid, and the critical age group, infant.

2. Exposure pathways from iodines and particulates are milk ingestion, ground contamination, and inhalation.

3. The radioiodine and particulate mix is based on the expected source term given in Table 1.1.

4. Real cow locations are not considered.

5. Deposition is calculated based on the curves given in Figure 1.5.

6. A milk cow obtains 100 percent of her food from pasture grass.

~fuattons t To from 1

calculate the dose from radiological effluents discharged a given release point for any one of the potential maximum-exposure points, the following equations are used:

. Inhalation Equation as for calculating air concentration, x, in the Noble Gas Section, 1.1.1.A.

is the same For determining the thyroid dose rate:

DTHI = 10 g xi DFIi (1.4) 1 where:

DTHI thyroid dose rate due to inhalation, mrem/yr.

xj air concentration of radionuclide i, ~Ci/m'.

DFI.1 infant inhalation dose factor. mrem/yr per qCi/cm', based on Regulatory Guide 1.109 dose conversion factors (mrem/pCi) and an assumed 1400 m'/yr infant breathing rate.

m'/cm'onversion factor.

2. Ground Contamination For determining the ground concentration of any nuclide:

G~ = 3.15 x 10' 7

~f~ I OR (2~x/n)Xi L'-exp-('k~ tg) ] (1. 5)

Y ~

where:

Gi = ground concentration of radionuclide i, qCi/m~.

- stability class.

= joint relative frequency of occurrence of winds in stability class k blowing toward this exposure point, expressed as a fraction.

Qi average release rate of radionuclide i,'>Ci/s.

E

DR relative deposition rate, m ~ (Figure 1'.6).

The choice of figures is governed by the effective release height calculation by equation l.la. A linear interpolation is used for effluent release heights that fall in between the given curves.

x - downwind distance, m.

n number of sectors, 16.

2~x/n = sector width at point of interest, m.

radioactive decay coefficient of radionuclide i, yr ~.

tb time for buildup of radionuclides on the ground, 35y.

3.15 x 10' s/yr conversion factor. "

For determining the thyroid dose rate from ground contamination:

OTHG

= (8,760) 10 $ Gi DFGi (1. 6) 1 where:

OTHG

= thyroid dose rate due to ground contamination, mrem/yr.

G = ground concentration of radionuclide i, >Ci/m'.

OFGi = dose factor for standing on contaminated ground, mrem/h per pCi/m'Table 1.7).

8,760 = occupation time, h/yr.

10+ = pCi/yCi conversion factor For determining the concentration of any nuclide (except H-3) in

'li '~Ei and on vegetation:

1 ~

7

~ (2 x/n) L 'f yfi Il,k,~'lj

+" P.;

where:

CV~ ~concentration of radionuclide i in and on vegetation, yCi/kg.

stability class.

frequency of this stability class and wind direction combinat1on, expressed as a fra'ction.

average release rate of radionucl1de 1, qCi/s.

DR relative deposition rate, m ~ (F1gure 1.6). The choice of figures is governed by the effective release height calculation by equation l.la. A linear interpolation is used for effluent release heights that fall in between the given curves.

downwind distance, m.

n' number of sectors, 16.

2~x/n = sector width at point of interest, m.

fract1on of deposited act1v1ty retained on vegetation, 0.47, consistent with NUREG/CR-1004.

>Ei = effective removal rate constant, xEi = xi + x~,

where:

= the radioact1ve decay coeffic1ent, h

= a measure of phys1cal loss of weather1ng

(+ = .0023 h and 0.0017

'or particulates for iodines).

te period over which deposition occurs, 720 h.

Yv agr1cultural yield, 1.18 kg/m~.

cC Biv transfer factor from so11 to vegetat1'on of radionuc lide i (Table 1.6) .

rad1oactive decay coeff1cient of radionuclide i, h ~

time for buildup of rad1onuclides on the ground, 3.07 x 10' (35 yr).

effective surface density of so11, 240 kg/m'.

3,6OO s/h conversion factor.

For determining the concentration of H-3 in vegetation:

CYT ~ l0~ xT (0.75)(0.5/H) (1.8) where:

CVT = concentration of H-3 in.,vegetation, qCi/kg.

air concentration of H-3, yC1/m'.

0.75 = fraction of total plant mass that is water, 0.5 = ratio of- trit1um concentrat1on in plant water to tritium concentration in atmospheric water.

H = absolute humid1ty of the atmosphere, .9 g/m'.

10' g/kg conversion factor.

For determ1ning the concentrat1on of any nucl1de 1n cow's milk:

CN; - CY; FNi Of exp (-X tf) (1.9) where:

CHi concentration of radionuclide i (including H-3) in cow's milk, yCi/K.

CVi concentrati on of r adi onuc 1 1 de i in and on vegetati on, yCi/kg.

transfer factor from feed to milk for radionuclide 1, d/K (Table 1.6).

Of amount of feed consumed by the cow per day, kg/d.

radioactive decay coefficient of radionuclide 1, d '.

transport t1me of act1vity from milk1ng to ingestion, 1 day For determining the thyroid dose rate from ingestion of cow's milk:

OTHM 10~ $ CMi DFIHGi UM (1 .10) where:.

DTHM thyroid dose rate due to milk ingestion, mrem/yr.

CMi = concentration of radionuclide i in cow's milk, yCi/K.

DFIHGi = infant ingestion dose factor, mrem/pCi, (Regulatory Guide l.109, Table E-14) y5 ~

UM infant ingestion rate for, milk, 330 t/yr.

pCi/qCi conversion factor.-

4. Total Th roid Dose Rate For determining the total thyroid rate from iodines I

dose and particulates:

0TH = OTHI, + OTHG + OTHM (1.11) where:

OTH

= total thyroid dose rate, mrem/yr.

OTHI = thyroid dose rate due to inhalation, mrem/yr.

DTHG

= thyroid dose rate due to ground contamination, mrem/yr.

DTHM = thyroid dose rate due to milk ingestion, mrem/yr.

The above dose calculations are repeated for each release point.

Dose rates from building vents are summed. The calculated thyroid dose rates from the vents and stack will then be used in step 2.

~ste 2 (setpoints)

The dose rate 11m1ts of interest (10CFR 20) are Total body - 500 mrem/yr Skin 3,000 mrem/yr Maximum organ = l,500 mrem/yr Dividing the above 11mits by the appropriate dose rates calculated, in step l yields the following ratios':

Dose Rate Limit Vent Dose Rate (step 1) l'tack Dose Rate Limit Dose Rate (step l)

These ratios, R;, represent how far above or below the guidelines the step 1 calculation was. Mult1plying the orig1nal source terms 9 by the appropr1ate rat1o Ri w111 give release rates, r;,

that will result in the dose rate 11mits g1ven above. ~

Instantaneous release rates (q;) for each. nuclide type and release point are now limited by the following equations:

For noble gas releases:

R1 + 22 < l l2 where ql = 1nstantaneous release rate from building exhaust vents in Ci/s.

= 1nstantaneous release rate from main stack in Ci/s.

q2 For iodines and particulates with half-lives > 8 days.

23 + QA<l r4 r3 where instantaneous release rate from build1ng exhaust vents in yCi/s.

q~ = instantaneous release rate from main stack in pCi/s.

To simplify the dynamic operation of the plant, the dose rate limits were transformed into conservative release rate limits based on hi stot ica~ource terms and meteorology. The values, listed below were used as administrative guidelines for'operation and development of alarm/trip setpoints (see Technical Instruction 15) to ensure that the instantaneous dose rate limits are not exceeded.

Airborne Noble Gas Iodine and Particulate Elevated 14.4 Ci/s 35.7 yCi/s Ground Level 0.15 Ci/s 2.19 pCi/s 1.2 Monthl Dose Calculations Dose calculations will be performed monthly to determine compliance with specifications 3.8.8.3 and 3.8.8.5. The specifications require that the dose rate in unrestricted areas due to gaseous effluents from each reactor at the, site shall be'imited to the following values:

For noble gases,

l. During any calendar quarter, 5 mrad to air for gamma radiation and 10 mrad to air for beta radiation.

t 2.

1.

2.

During any calendar year, 10 mrad to air 20 mrad to air for beta radiation.

For iodines and particulates, for During any calendar quarter, 7.5 mrem to any organ.

During any calendar year, 15 mrem to any organ.

gamma radiation and This section of the ODCM describes the methodology that will be used to perform these monthly calculations.

Doses will first be calculated by a simplified conservative approach (step 1). If these exceed these limits, a more realistic calculation will be performed (step 2).

1.2.1 Noble

~ ~ Gases

~Ste 1 Doses will be calculated

~

using the methodology described in this step. If 50>> of the applicable limits are exceeded, step 2 wi'll be per f ormed.

Equations and assumptions for calculating doses from releases of noble gases are as follows:

Assumotions

1. Doses to be calculated are gamma and beta air doses.

2. The behest annual-average x/0 based on licensing meteorology for any offsite location (not necessarily a site boundary location) will be used. Elevated meteorology is assumed for stack releases. All other vent releases assume ground level meteorology.

3. Ho credit i s taken for radi oacti ve decay.

t

4. For gamma and beta doses, releases of Ar-41, Kr-85m, Kr-85, Kr-87, Kr-88, Xe-131m, Xe-133m, Xe-133, Xe-135, Xe-135m, and Xe-138 are considered.

5. Dose factors are calculated using data from TVA's nuclide library.

6. The dose calculations are extrapolated assuming that only 90 percent of total dose was contributed.

7. A semi-infinite cloud model is used.

8. Building wake effects on effluent dispersion are considered.

~Eeet1ons For determining the gamma dose to air:

DY= Q/~ 10~

Oj OF (1.12) 09 315 x10v K where:

Dy gamma dose to air from continuous releases, mrad.

x/0 highest annual-average relative concentration, 1.84 x 10 '/m'ground level) 2.08 x 10 '/m'elevated) 0.9 fraction of total gamma dose expected to be contributed by these nuclides.

10~ yGi/Ci conversion factor 3.15 x- 10~ s/yr conversion factor 4

Qi = monthly release of radionuclide i, Ci.

OFy-1 galena-to-air dose factor for radionuclide i, mrad/yr per >Ci/m'Table 1.5). For Kr-88 and Xe-138, the dose factors for Kr-88+0 and Xe-138+0 are used to account for daughter buildup.

This equation then reduces to Oy = 6.49 x '10 ' Qi OFyi (ground level) (1.13) 1 J)y = 7.34 x 10-10 Qi DFyi (stack) ~

(1.14) 1 For determining the beta dose to air:

6

~/( 10~ g Qi DFG (1.15) 0.9 3.15 x 107 1 where: Og = beta dose to air, mrad. x/Q = highest annua,l-average relative concentration, 1.84 x 10 ~ (ground level) 2.08 x 10 'elevated) 0.9 = fraction of total beta dose expected to be contributed by these nuclides. 10' yCi/Ci conversion factor 3.15 x 10' s/yr conversion factor Qi = monthly release of radionuclide i, Ci. OFgi = Beta-to-air dose factor for radionuclide i, mrad/yr per pCi/m'Table 1.5). For Kr-88 and Xe-138, the dose factors for Kr-88+0 and Xe-138+D are used to account for daughter buildup. This equation then reduces to: 0> 6 49 x 10-s g Qi DF (ground level) (1.16) 1 7.34 x 10 ~~ (stack) (1.17) Dg = K Qi OFO 1 S~te 2 This method~gy is to be used if the calculations in Step 1 yield doses that exceed 50% of the applicable limits. Equations and assumptions for calculating doses to air from reIeases of noble gases are the same as those in Section 1.1.1, Step 1, Part A, with the following exceptions:. Assum tions

l. Ooses to be calculated are gamma and beta air doses.

2. Oose is to be evaluated at the nearest site boundary point in each sector and at other locations expected to be maximum exposure points.

r

3. Historical onsite meteorological data for the appropriate months from the period 1977-1979 will be used.

4. Releases from the radwaste and reactor buildings are treated as .

level. 'plit

5. Raw meteorological data for ground level portion of the split level UFO consist of wind speeds and directions me'asured at the 10m level and temperature measurements at 10m and 45m. The elevated portion of the split level JFO is based on wind speeds and directions measured at the 46m level and temperature measurements at 45m and 90m.

6. All measured radionuclide releases are considered.

7. A semi-infinite cloud mode1 is used.

8. Radioactive decay is considered.

9. Building wake effects on effluent dispersion are'considered.

10. Oose factors are calculated using data from TVA's radionuclide library.

~Euatioee Equations for calculating air concentration, x, is the same as in Section 1.1.1, step 1, part A. Air concentrations are calculated for the site boundary in each sector. For determining the gamma dose to air Oqn = tm E xni OF>i {1.18) 1 where: D~n garana dose to air for sector n, mrad. xni air concentration of radionuclide i in'sector n, yCi/m~. DFY galena-to-air dose factor for radionuclide i, mrad/yr per pCi/m'Table 1.5.). time period considered, yr. For determining the beta dose to air: 00n =, tm $ xni OFO (1.19) 1 where: D0n = beta dose to air for sector n, mrad. xn; = air concentration of radionuclide i in sector n, yCi/m~ t beta to air dose factor for radionuclide i, OFB- = mrad/yr per qCi/m'Table '1.5) tm = time period considered, yr The sector having the highest total dose is then used to check compliance with specification 3.8.B.3. 1.2.2 Iodines and Particulates ~Ste 1 Ooses will be calculated using the methodology described in this step. If 50~ of the applicable limits are exceeded, step 2 will be perf ormed. Equations and assumptions for calculating doses from releases of iodines and particulates are as follows: ssum tions

1. Oose is to be calculated for the infant thyroid from milk ingestion and for the child bone and teen g.i. tract from vegetation ingest1on.

2. Real cow locations are considered for the milk pathway and nearest resident-locations with home.-use gardens are considered for the vegetable pathway.

3. The highest annual-average x/Qs and 0/Qs for any location (not necessarily a site boundary location) are used based on licensing methodology. Elevated meteorology is assumed for stack releases. All other vent releases assume ground level meteorology.

5. Releases of H-3, I-131 and I-133 are considered for the milk pathway. H-3, Sr-89, Sr-90, Cs-134 and Cs-137 releases are considered for the vegetable pathway to the child bone.

H-3, Co-58 and Co-60 releases are considered for the vegetable pathway to the teen g.i. tract.

6. The dose calculations are extrapolated assuming that only 90 percent of the total dose was contributed.

7. The cow is assumed to graze on pasture grass for the whole year.

~Eeet1ens For determining the thyroid dose from milk ingestion: z(Qi OF i ) 0/Q x 106 + (QTOFT) x/Q OTH = (1.20) 0.9 x 3.15 x 10~ where: OTH = thyroid dose from H-3, I-131, and I-133, mrem. Qi = monthly release of iodine nuclide i, Ci. QT . monthly release of H-3, Ci. OF> nuclide i milk ingestion dose factor to infant, . 7.24 x 10~~ mrem/yr per yCi/m'-s for:$ -131 and 1.52 x 10'~ mrem/yr per qCi/m'-s for I-133 with Regulatory Guide 1.109 and NUREG/CR-1004 'consistent methodologies).

DFT = H-3 milk ingestion dose factor, 3.53 x 10'rem/yr per yCi/cc (consistent with Regulatory Guide 1.109 and NUREG/CR-1004 methodologies). 0/Q = relative deposition rate, 2.30 '~ 3.16 x 10 ' x 10

                                                    'ground level) m
                                                                                 'stack),

x/Q relative air concentration, 1.69 x 10 1.47 x 10 s/m'ground lev&) '/m'stack),

                                               ~ '0 0.9        fraction of dose expected to be contributed                                         by H-3, I-131,  and   I-133.

3.15 x 10' s/yr. 10~ = yCi/Ci Equation 1.20 then reduces to: OTH = 8.11 x 10 " E Qi OFi + 2.10 x 10 'T (stack)

       = 1.11 x 10    "    1 E

1 Qi DF. + 1.83 x 10 'T (ground level) For determining the bone dose from vegetable ingestion: Z(Q;DF;) 0/Q x 10'+ QTDFT X/Q OBC (1.21) 0.9 x 3.15 x 10~ where: DBC bone dose to child, mrem. Qic monthly release of particulate nuclide i, Ci. QT monthly release of H-3, Ci. DF vegetable ingestion dose factor to child, 2.25 x 1011, 1.36 x 10", 1.59 x 10~'; and 2.58 x 10'~ mrem/yr per yCi/m'-s for Sr-89, Sr-90, Cs-134, and .Cs-137, respectively (consistent with Regulatory Guide 1.109 and NUREG/CR-1004 methodologies). DFT vegetable ingestion dose factor for H-3, 4.53 x 10~ mrem/yr per yCi/cc D/Q relative deposition rate, 1.05 x

                              '                          10  ', m ~  (stack),

5.29 x 10 'ground level) X/Q relative air concentration, 9.50 1.84 x 10 ~ s/m'ground level) x 10 '/m'stack), 3.15 x 10'/yr. pCi/Ci 0.9 fracti'on of total bone dose expected to be contributed by H-3, Sr-89, Sr-90, Cs-134, and Cs-137 Equation 1.21 then reduces to:

                                             ~ p 3.70 x  10-"   Z  Qi OFi +    1.52 x 10-'T     (stack) 1
            = 1.87 x 10   '

1 Qi OFi + 2.94 x 10 'T (ground level) For determining the gastrointestinal (g.i.) tract dose from vegetable ingestion: DGIT = E(Q.OF.) 0/Q x 10' 0.9 x 3.15 x 10'1.22) (QTOFT) X/Q where: OGIT = teen g.i. tract dose from H-3, Co-58, and Co-60, mrem Q; = monthly release of cobalt nuclide i, Ci. QT monthly release of H-3, Ci DFi vegetable ingestion dose factor for the teen g.i. tract, 3.87 x 10'rem/yr per qCi/m'-s for Co-58 and 3.31 x 10'~ mrem/yr per qCi/m'-s for Co.-60 (consistent with Regulatory Guide 1.109 and HUREG/CR-1004 methodologies). DFT = vegetable ingestion dose factor for H-3, 2.92 x 10'rem/yr per yCi/cc (consistent with Regulatory Guide 1.109 and HUREG/CR-1004 methodologies). D/9 = relative deposition rate, 1.05 x '10 ' ~ (stack), 5.29 x 10 ~ m 'ground level) X/(} = relative air concentration, 9.50 x 10,'/m'stack), 1.84 x 10 '/m'ground level) 3.15 x 10' s/yr 10~ = pCi/Ci 0.9 fraction of total g.i. tract dose expected to be contributed by H-3, Co-58, and Co-60 Equation 1.22 then reduces to : DGIT 3.70 x 10 " E (giDFi) + 9.78 x 10='T (stack) 1.87 x 10 ~ Z (giDF.) +'"1.90 x 10 0T (ground level) 1 ~Ste 2 This methodology is to be used if the calculations in step 1 yield doses that exceed 50$ of the applicable limits. Doses for releases of iodines and particulates shall be calculated using the methodology in Section 1.1.1, step 1, part 8, with the following exceptions:

l. All measured radionuclide releases will be used.

2.. Dose will be evaluated at real cow locations and will consider actual grazing information.

3. Releases from the radwaste and reactor buildings are treated as split-level.

4 ~ Raw meteorological data for the ground level portion of the split level JFO consist of wind speeds'nd directions measured at the 10m 'level and temperature measurements at 10m and 45m. The elevated portion of the split level JFD is based on wind speeds and directions measured at the 46m level and temperature measurements at 45m and 90m. The receptor having the highest total dose is then used to check compliance with specification 3.8.8.5.

                                            -,24-

t 1.3 A uarterl and Annual Dose complete dose analysis utilizing II Calculations 7 the total estimated" gaseous releases for each calendar quarter will be performed and reported as required in the Technical Specification 6.7.5. Methodology for this analysis is the same as that described .in Section 1.1.1, except that real pathways and receptor locations (Table 1.4) are considered and releases from the radwaste and reactor buildings are treated as split level. Also, raw meteorological data for ground level releases consist of windspeed and direction measurements at 10m and temperature measurements of 10m and 45 m. The ground level portion of the split level 3FD consist of wind speeds and directions measured at the 10m level and temperature measurements at 10m and 45m. The elevated portion of the split level JFD is based on wind speeds and directions measured at the 46m level and. temperature measurements at 45m and 90m. Windspeeds and directions for elevated releases are measured at 93m. Stability class D is assumed to persist during the entire period for elevated releases. In addition, meteorological data representative of each corresponding calendar quarter will be used. This analysis will replace the estimates in Section 1.2. At the end of the year an annual dose analysis will be performed by calculating the sum of the quarterly doses to the critical receptors.

1.4 Gaseous Radwaste Treatment S stem 0 e'ration The gaseous radwaste treatment system (GRTS) described below'hall be maintained and operated to keep releases ALARA. 1.4.1 S stem Desci i tion A flow diagram for the GRTS is given in Figure 1.3. The system includes the subsystems that process and dispose of the gases from the main condenser air ejectors, the startup vacuum pumps,.and the gland seal condensers. One gaseous radwaste treatment system is provided for each unit. The processed gases from each unit are routed to the plant st'ack for dilution and elevated release to the atmosphere. The air-ejector off-gas line of each unit and the stack are continuously monitored by radiation monitors. 1.4.2 Dose Pro'ections Doses will be projected monthly in accordance with the procedures in. the plant's Radiological Effluent Manual (REM). This will be done by averaging the calculated dose for the most recent month and the calculated dose for the previous month and assigning that average dose as the projection for the current month. These doses will be used to monitor radwaste system performance. 2.0 Li uid Effluents 2.1 Release Rate Limit Methodolo 2.1.1 RETS Re uirement Specification 3.8.A.l of-the Radiological Effluent Technical Specifications (RETS) requires that the concentration of radioactive material released at any time from the site to unrestricted areas (Figure 2.1) shall be limited to the Maximum Permissible Concentration (MPC) specified in 10 CFR 20, Appendix 8, Table II, Column 2 for nuclides other than dissolved or entrained noble gases. For dissolved or entrained noble gases, the concentration shall be limited to 2xl0 'Ci/ml total activity. To ensure compliance, the following approach will be used for each release. 2.1.2 Prerelease Anal sis Prior to release, a grab sample will be analyzed to determine the concentration (C;) of each gamma emitting radionuclide i in the radwaste tank. The following equation is used to calculate MPC fractions (Mi). C MPCi (2.1) where: MPC fraction of radionuclide i. Ci = concentration of radionuclide i in the radwaste tank, yCi/mK. MPCi = MPC of radionuclide i as specified in Section 2.1.1, yCi/mi. t The sum of the ratios (R) relationship: will be calculated by the following (2.2) where:

                = the  sum  of the ratios.
 ~    M         = HPC  fraction from equation 2.1.

2.1.3 Release Flow Rate Calculations There is one liquid release point into the discharge canal by one of-three possible modes: open 3 pumps 9 200,000 gpm/pump Oischarge helper 3 pumps 8 180,000 gpm/pump conduit closed 50,000 gpm 1 The sum of the ratios at the diffuser pipes must be < 1 due to the from the above source. The following relationship will assure this criterion is met:

                                                                           'eleases f (R 1)   < F                          (2.3) where:
                = the effluent flow rate (gallons/minute) before dilution.

R = the sum of the ratios as determined by Equation 2.2. F = minimum dilution flow rate for prerelease analysis. The allowable release rate is calculated before each release and the release rate is continuously monitored during the release so that the HPC limit is not exceeded. 2.2 Instrument Set pints 2.2.1 Set oint Determination The setpoint for each liquid effluent monitor will be established using plant instructions. Concentration, flow rate, dilution, principal gamma emitter, geometry, and detector efficiency are combined to give an equivalent setpoint in counts per minute (cpm). The locations and identification numbers for each liquid effluent radiation detector are shown in figures 2.2 and 2.3. The respective alarm/trip setpoints will be set such that Equation 2.3 is satisf'ied. The methodology describing the setpoint determination is contained in Technical Instruction 45. 2.2.2 Post-Release Anal sis A post-release analysis will be done using actual release data to ensure that the limits specified in Section 2.1.1 were not exceeded. A composite list of concentrations (Ci) by isotope, will be used with actual liquid radwaste (f) and dilution (F) flow rates (or t volumes) during the release. The data will be substituted into Equations 2.1, 2.2 and 2.3 to demonstrate compliance with the limits in Section 2.1.1. This data and setpoints wi 11 be recorded in auditable records by plant personnel. 2.3 Dose 2.3.1 RETS Re uirements Specification 3.8.A.3 of the Radiological Effluent Technical Specifications (RETS) requires that dose or dose commitment to an individual from radioactive material in liquid effluents released to unrestricted areas (Figure 2.1) from each reactor shall be limited:

    'a ~    During any calender quarter to < 1.5 mrem  to the total body and to < 5 mrem to any organ, and

b. During any calendar year to < 3 mrem to the total body and to < 10 mrem to any organ.

To ensure compliance,'umulative dose calculations wilp be performed at least once per month according to the following methodology. 2.3.2 Monthl Anal sis Principal radionuclides wi 11 be used to conservatively estimate the monthly contribution to the cumulative dose. If the projected dose calculated by this monthly method exceeds the monthly fraction of the annual limits in section 2.3.1, then the methodology in Section 2.3.3 will be implemented. The 20 nuclides (listed below), based on operational source terms, contribute more than 95 percent of the total estimated dose to the total body and the most critical organ for both the water and fish .ingestion pathways. The organs considered for both water ingestion and fish ingestion are the gastrointestinal tract (GIT), bone, thyroid, and liver. 8-3 Fe-59 Sr-90 2-1 31 Ha-24 Co-58 '2r/Hb-95 . I-133 Cr-51 Co-60 Mo/Tc-99m Cs-134 Mn-54 Zn-65 Ag-110m Cs-136 Fe-55 Sr-89 Sb-124 Cs-137 A conservative calculation of the monthly dose will be done according to the following procedure. First, the monthly operating report containing the release data will be obtained and the reported (if any) for of the above 20 radionuclides

~ ~

each 'ctivities will be noted. This~ information will 'then be used in the following calculations.

          ~
                ~

2.3.2.1 Mater In estion

 ~ ~   ~

The dose to an individual from ingestion of water is described

             ~
                        ~                ~

by the following equation. ~ 20 Djk ~l0~ 7 i~1 (DCF)ijk Iikmrem (2 4) where: dose for the jth organ and the kth age group from the 20 radionuclides, mrem. the organ of interest (bone. GIT, thyroid, liver or total body). the age group being considered, child or. adult. 0.95 conservative correction factor, considering only 20 radi onuc i des. 1 OCFijk ingestion dose commitment factor for the ith radionuclide for the jth organ for the kth age group, rem/qCi (Table 2.1)

     >ik          monthly activity ingested of the          ith radionuclide   by the kth age group, yCi.

conversion from rem to mrem. The activity ingested due to drinking water, lik, is described by: F d (7.34 x 10") o QCi (2.5) where:

               =  activity     released of    ith radionuclide    during the month, yCi.
               = maximum     individual water consumption rate corresponding to the kth age group.

(Adult = 2000 ml/d; Child = 1400 ml/d, from Regulatory Guide l.l09) 30 = days per month F average river flow rate for the month (cubic feet per second) d fraction of river flow available for dilution (0.20) 7.34 x 10~~ conversion from cubic feet per second to milliliters per month Inserting this for Iik in equation 2.4, the dose equation for water ingestion then becomes: 20 (2 6) 2.3.2.2 Fish In estion The dose to an individual from the consumption of fish is described by Equation 2.4. In this case the activity ingested of the ith radionuclide due to eating fish (Iik) i is described by

Ai Bi~H (2.7) Fd (7.34 x 10' where: 1 Ai = activity released of the ith radionuclide during the month, yCi B = effective fish concentration factor of ith radionuclide, >Ci/g per yCi/ml. (Table 2.2.)

                = amount   of fish eaten monthly by the kth age group (adult  = 1750 g,  child = 575 g, Regulatory Guide 1.109).
                = average   river flow rate for the  month, cubic   feet per second.

t d = fraction of river flow available for dilution, 0.20. 7.34 x 1010 = conversion from cubic feet per second to milli liters per month. Inserting this for Iik in equation 2.4, the dose equation for fish ingestion then becomes:

t 2.3.2.3 Recreation For the recreation dose calculation, the total dose is".estimated based on a calculation of the shoreline dose for Co-58, Co-60, Cs-134, and Cs-137. The shoreline dose due to these four nuclides is expected to contribute over 95 percent of the total recreation dose. The total body and maximum organ dose to an individual via-the shoreline recreation pathway are assumed to be equal. The recreation dose is described by the following equation: 1 0.95 4 g

                          ~ROCF        i~i~67 8760                                            {2.9) where:

D= recreation dose from plant releases, r mrem. 0.95 = conservative correction factor for considering only 4 radionuclides. ROCFi = shoreline recreation dose commitment factor for the ith radionuclide, mrem/yr per 2.3).(Note: For Cs-137, the dose commitment

                                                       >Ci/cm'Table factor for its daughter, Ba-137m, is assumed.).

0 = concentration of ith radionuclide in shoreline sediment, yCi/cm', as described by the following equation (based on equation A-5 in Regulatory Guide 1.109). 100 ~ RHLi ~ Ci ~ M [1 - exp(-nit)] - 0.1 (2.10) where: 100 = transfer constant defined in Regulatory Guide 1.109 equation A-4. RHL = radiological half-life of the ith radioisotope, days (Table 2.1). C = concentration of ith radionuclide in the, Tennessee River, yCi/ml.

                     =  Ai/(F    ~ d -  7.34 x 10~~)

where: A activity released of ith radionuclide during the month, yCi.

                             =-average river flow for the month, cubic feet per second.

d fraction of river flow available for dilution, 0.20.- 7;34 x-10>> = conversion from cubic feet per second to milli liters per month.

                       = shoreline width factor, 0.3 for a lake shore, per Table A-2 Regulatory Guide 1.109.

decay constant of the ith radionuclide, yr '. buildup time in 'sediment, assumed 15 years,.per Regulatory Guide 1.109. 67 - assumed monthly exposure time for maximum individual,

                = 500 h/yr = (-10 h/week) x 0.4 (fractional exposure for worst quarter + 3 (months/quarter)).

8760 = conversion from year to hours. 0.1 = conversion factor, combining the conversions from cm'nd to m'o ma K. The recreation dose equation then becomes: D}(Oe00692A1+Oe00012A2+Oo00206A3+ 0 00342A4)(2ell) t where: Al, A2, A3, A4, = the activities of Cs-137, Co-60, Co-58, Cs-134, and respectively, yCi. 2.3.2.4 Month 1 Sunma To obtain the total monthly dose to the total body, sum the total body dose from water ingestion, the total body dose from fish ingestion, and the recreation dose. This value wi 11 be compared to the Technical Specification limit for total body dose. To obtain the total monthly dose to the maximum organ, sum the maximum organ dose from water ingestion, the maximum organ dose from fish ingestion, and the recreation dose. This value will be compared to the Technical Specification limit for maximum organ dose. .Calendar quarter doses are first estimated by suoming the doses calculated for each month in that quarter. Calendar year doses are first estimated by summing the doses calculated for each month in that year. However, if the annual doses determined in this manner exceed or approach the specification limits, doses calculated for previous quarters with the methodology of Section 2.3.2 will be used instead of those qGarterly doses estimated by summing monthly results. An annual check will be made to ensure that the monthly dose estimates account for at least 95 percent of the dose calculated by the method -. ~ described in Section 2.3.3. If less than 95 percent of the dose estimated, either a new list if principal isotopes will be has'een prepared or a new correction factor wi 11 be used. The latter option will not be used if less than 90 percent of the total dose is predicted. 2.3.3 uarterl and Annual Anal sis' complete analysis utilizing the total estimated liquid releases for each calendar quarter will be performed and reported as required in Section 6.9 of the Technical Specifications. This analysis will replace previous estimates calculated using Section 2.3.2 methodology and will also include an approximation of population -

                                                                           'oses.

2.3.3.1 Individual Doses .The dose, Djk, to the maximum individual from n nuclides is described by: 5 n Djk g $ Dijkm, rem (2.12) m=1 i=1 n 2 5 f (DCF) i jk ~ Iikm~ + g [(ROCF) i jm Vim ~ Tm v], rem (2.13) i 1 m=1 m=3 where: Dl jkm dose to the jth organ for the kth age group from the ith radionuclide via the mth exposure path . the organ of interest (bone, GI tract, thyroid, liver, total body and skin).

                =  the age group being considered: adult or child for the ingestion pathways; adult for the recreation pathways.

exposure pathway of interest:

1. water ingestion,

2. fish ingestion,

3. shoreline recreation,

4. above water recreation, and

5. in-water recreation.

              - = ingestion dose commitment factor for the jth organ (DCF)ijk from the ith radionuclide for the kth age group, rem/qCi. Table 2.1 is a list of ingestion dose factors for the two age groups.

Iikm The activity ingested of the ith radionuclide, via the mth exposure pathway for the kth age group, yCi. Far the water ingestion pathway: ikl Cl k (2.14) For the fish pathway: Iik2 ~ Ci Bi Mk (2.15) where: C; concentration of the ith radionuclide during the release period, qCi/mR Ai/(FLd). where: A = Activity released of ith radionuclide during the release period, yCi. FL = Total river flow at location L during period, mR.

                     =   Location of interest (For dose to the maximum individual the first down-river exposure point is used.       For the population  .

dose, various down-river locations are used to account for the total exposed population. Table 2.4a gives the river location of public water supplies; Tables 2.4b and 2.4c give the boundaries of the various reaches in which concentrations are calculated for the fish and recreation pathways).

                     =   fraction of river flow available for di luti on (0. 20 above Wheeler 0am, l,below the dam) .
            =  average rate of water consumption for the kth age group, per Regulatory Guide 1.109
            =  for  maximum individual:

adult 2000 mR/d child 1400 mR/d

            =  for  average    individual (population):

adult - 1010 mR/d child 710 mR/d. H = number of days during the release period, day. Bi = bioaccumulation factor for the ith radionuclide in fish, >Ci/g per >Ci/mR, (Table 2.2). Hk amount of fish consumed during the period for the kth age group (fraction of year times the annual consumption rate per Regulatory Guide 1.109) for maximum individual: adult 21 kg/yr child 6.9 kg/yr for average individual (population): adult 6.9 kg/yr child 2.2 kg/yr. RDCF) ijm = recreation dose commitment factor for the jth organ from the ith radionuclide via the mth pathway; mrem/yr per concentration (gim) in medium, (Table 2.3). the concentration of the ith radionuclide in the environmental medium pertaining to mth pathway. for above-water and in-water recreation pathways:

        ~im  ~i5  Ci For the shoreline recreation pathway:

gi3 100 ~ RHLi ~ Ci ~ H [1-exp(-ki ~ t) l (2.16) where: 100 = transfer constant. as defined in Regulatory Guide 1.109 equation A-4. RHLi = radiological half-life of the ith isotope, days, (Table 2.1) .

                   =  shoreline width factor (0.3 for a lake shore, per Tab e A-2 of Regul ator y Gui de 1.109) .

1

                   =  decay constant of the ith radionuclide 0.693/RHL t          =  buildup time in sediment, assumed 15 years, per Regulatory Guide 1.109.

Tm = assumed exposure time of maximum individual for the mth pathway (3) shoreline 500 h/yr (-10 h/week) (4) above-water 1800 h/yr (6 h/d, 300 d/yr) (5) in-water 920 h/yr (6 h/d, for five summer months). Fraction of annual exposure for each quarter 1st Quarter January-Harch 0.1 2nd Quarter Apri 1-June 0.3 3rd Quarter July-September 0.4 4th Quarter October-December 0.2.

2.3.3.2 Po ulation Ooses 0 The total dose, hj, from all 5 pathways to the jth organ of the population from n nuclides at p locations -is described by: p 5 n hj= g g g hijml, man rem (2.17) 1~1 m 1 i~1 p 5 n 4j= g $ $ .Oijml - Pml, man-rem (2.18) 1=1 m=1 i =1 where: hi jml Dose to the jth organ of the total po'pulation from the ith radionuclide via the mth pathway at location l. Dijml = Dose to individual (as described in-Section 2.3.3.1) at location l. Pl = Number of people at location 1 (Table 2.4a-c). The population is assumed to consist of 71-percent adults and 29-percent children (from Appendix 0, Regulatory Guide 1.109, the value for children includes teenagers). 2.4

~   0   erabilit of   Li uid Radwaste E ui ment Radiological Effluent Manual (REM) requires that the liquid
         ~    ~

The radwaste system (Figure 2.3) shall be used to reduce the radioactive

                    ~
                            ~

materials in liquid wastes prior to their discharge when the

projected dose due to liquid effluent releases* to unrestricted areas (see Figure 2.1) when averaged over 31 .days would exceed 0.06 mrem to the total body or 0.21 mrem to any organ. Doses will be projected monthly to assure compliance. 2.5 Dose Pro ections In accordance with the REM, dose projections wi 11 be performed. This will be done by averaging the calculated dose for the most recent month and the calculated dose for the previous month and assigning that average dose as the projection for the current month. "Per operating reactor unit.

3. 0 Radi o 1 o i ca 1 Environmenta 1 Moni to rin 3.1

   ~        Monitorin Pro
                ~

ram environmental radiological monitoring program as described in

          ~                                  ~                        ~   ~

An Tables 3.1 and 3.2 and in Figures 3.1, 3.2, 3.3, and 3.4 shall be

                                 ~    ~
                        ~                       ~     ~  ~  ~ ~

conducted. Results of this program shall be reported in accordance with Section F-1 of the REM. The atmospheric environmental radiological monitoring program shall consist of 10 monitoring stations from which samples of air particulates and radioiodine shall be collected. The terrestrial monitoring program shall consist of the collection of vegetation, milk, soil, drinking water, and food crops. In addition, direct galena radiation levels will be measured at 40 or more locations in the'icinity of the plant. The reservoir sampling program shall consist of the, collection of samples of surface water, sediment, and .fish. Oeviations are permitted from the required sampling schedule if specimens are unobtainable due to hazardous conditions, sample or malfunction of sampling equipment. If the latter, 'navilability, every effort shall be made to complete corrective action prior to t the end of the next sampling period. 3.2 Oetection Ca abilities Analytical techniques shall be such that the detection capabilities listed in Table 3.3 are achieved. 3.3 Nonroutine Reool ts Honroutine reports shall be submitted pursuant to Section F-3 of the REM. 4.0 Annual Maximum Individual Ooses Total determine compliance with 40 CFR 190, the annual dose contributions

To to the maximum individual from SFH radioactive effluents and all other

           ~        ~  ~

nearby uranium fuel cycle sources will be considered.-, The annual dose to the maximum individual will be conservatively estimated by: first, sumning the total body air submersion dose, and the critical organ dose

    ~                     ~

from gaseous effluents;,the total body dose, and critical organ dose from liquid effluents for each quarter. in accordance with sections .1.3 and 2.3.3 Then to this sum for each quarter'is added any identifiable increase in direct radiation dose levels attributable to the plant as determined by the environmental monitoring program outlined in section 3.0. These quarterly sums are then conservatively summed for the four calendar quarters to estimate the maximum individual dose for the year.

TABLE 1.1 Expected Annual Routine Atmospheric Releases from One Unit at BFN Nuclear Plant Ci/ r/Unit Stack Ci/ r/Unit Reactor Radwaste Turbine Gland Complex Building Building Seal and

 ~Isoto e           Vent            Vent             Vent        ~off  as          MVP Kr-85m                6E+0           <  1              2E+0      1.66E+4          O B OE+0 Kr -85                                                            6.3E+2 Kr-87                 6E+0           <  1           9.5E+1       7.47E+2          O.OE+0 Kr-88                 9E+0                         1.02E+2       1.35E+4          O.OE+0 Kr-89                 lE+0         3.4E+1          5.03E+2       4.10f+3          O.OE+0 Xe-131m                     'E+0

3. 09E+2 O.OE+0 Xe-133m 6.0E+1 Of+0 8.51E+2 0. OE+0 ~

Xe-133 1.03E+2 2.94E+2 5.81E+2 p9.47E+4 3.0E+2 Xe-135m 1.11E+2 6.67F+2 4.64E+2 9.17E+2 O.OE+0 Xe-135 1.73E+2 3.28E+2 '.72E+2 5.99E+2 2.0E+2 Xe-137 7.BE+1 1.13E+2 3.86E+2 5.04E+3 0.Of+0 Xe-138 1.2E+1 2f+0 1.18E+3 3.15E+3 - 0.0E+0 I-131 I 5.94E-2 5.0E-3 1.56E-2 4.1E-3 8.5E-3 I-1 32 I 5.94E-1 5.0E-2 1.79E-1 4.69E-2 9.73E-2 I-1 33 I 2.97E-1 2.5E-2 1. 23f-1 3.23E-2 6.71E-2 I-134 I 1.49E+0 1.25f-l 2.67E-2 7.0E-3 1.45E-2 I-1 35 I 5.94E-1 5.0E-2 1.23E-l 3.23E-2 6.71E-2 I-1 31 0 3.16E-2 2.9E-2 6.5E-3 3.32E-2 2.74E-1 I-1 32 0 3.16E-l 2.9E-l 7.44E-2 3.80E-1 3.14E+0 I-1 33 0 1.58f-l 1.45f-l 5,13E-2 2.62E-l 2.16E+0 I-134 0 7.90E-1 7.25E-1 l.llf-2 5.68E-2 4.69E-1 I-135 0 3.16E-l 2.90E-1 5.13E-2 2.61E-l 2.16E+0. Cr-51 3E-3 9E-4 lE-3 1E-4 O.OE+0 Mn-54 3E-3 5E-3 2E-3 4E-5 O.OE+0 Co-58 2E-3 4EH 9E-5 2E-5 O.OE+0 Fe-59 1E-4 8E-4 4E-4 2E-4 O.OE+0 Co-60 3E-2 6E.-3 3E-3 lf-5 O.OE+0 Zn-65 3E-3 2E-4 4E-4 9E-5 O.OE+0 Sr-89 lE-2 3E-1 O.OE+0 . Sr-90 2E-3 4E-3 O.OE+0 Hb-95 3E-4 2EH 9E-6 BE-5 0.0E+0 Sr-95 1 f& 1 f-4 BE-6 8E-5 O.OE+0 Ru-103 3E-5 1E-4 2EW lf-4 O.Of+0 Ag-110m 7E-6 O.OE+0 Sb-124 3E-5 3E-4 6E-5 BE-5 O.OE+0 Cs-134 5E-3 3E-4 5E-4 2E-5 O.OE+0 Cs-136 2E-3 5E-5 1E-4 9E-8 O.OE+0 Cs-137 7E-3 4E-4 2E-3 7E-4 O.OE+0 Ba-140 4E-3 5EH 2E-2 BE-3 0.0E+0 Ce-141 4E-4 2E-4 2f-3 2E-5 O.OE+0 Ce-144 5E-6 4E-6 O.OE+0 Ar-41 2.5E+1 OE+0 OE+0 OE+0 O.OE+0 C-14 Of+0 Of+0 OE+0 9.5E+0 O.OE+0 H-3 Of+0 9.5E+0 OE,+0 OE+0 O.OE+0

Hot avai lable.

enotes nonorganic iodine (elemental, particulate, HIO). organic iodine.

TABLE 1.3 (Sheet 1 of 22) JOINT PERCENTAGE FRE UEHCIES OF WIND SPEED BY WIND DIRECTION FOR STABILITY CLASS A (DELTA-T< -1.9'C/100 H) BROWNS FERRY NUCLEAR PLANT JAN 1, 77 DEC 31, 79 WIND WIND SPEED (HPH) Dl RECTION 0:6-1. 4 1. 5-3. 4 3.5-5.4 5.5-7.4 7.5-12.4 12.5-18.4 18.5-24.4 >=24.5 TOTAL H 0.0 0.0 0.0 0.04 0.12 0.05 0.0 0,0 0.21 NHE 0.0 0.0 0.0 0.05 0.19 0.10 0.0 0:0 0.34 NE 0.0 0.0 0.0 0.04 0.06 0.0 0.0 0.0 0.10 ENE 0.0 0.0 0.0 0.01 0.0 0.0 0.0 0.0 0.01 E 0.0 0.0 0.0 0.0 0.01 0.0 0.0 0.0 0.01 ESE 0.0 0.01 0.11 0.17 0.02 0.0 0.0 0.0 0.31 SE 0.0 0.03 1.11 0.40 0.02 0.0 0.0 0.0 1.56 SSE 0.0 0.04 0.52 0.10 0.02 0.0 0.0 0' 0.68 S 0.0 0.01 0.38 0.11 0.04 0.0 0.0 0.0 0.54 SSW 0.0 0.0 0.04 0.05 0.01 0.0 0.0 0.0 0.10 SW 0.0 0.0 0.05 0.04 0.0 0.0 ', 0.0 0.0 0.09 WSW 0.0 0.0 0.04 0.07 0.04 0.0 0.0 0.0 0.15 W 0.0 0.0 0.01 0.05 0.05 0.01 0.0 0.0 0.12 WHW 0.0 0.0 0.02 0.03 0.09 0.06 0.0 0.0 0.20 HW - 0.0 0.0 0.0 0.02 0.17 0.11 0.0 0.0 0.30 HHW 0.0 0.0 0.01 0.01 0.06 0.09 0.02, 0.0 0.19 SUBTOTAL 0.0 0.09, 2.29 1.19 0.90 0.42 0.0 4.91 TOTAL HOURS OF VALID STABILITY OBSERVATIONS 25935 TOTAL HOURS OF STABILITY CLASS A 1262 TOTAL HOURS OF'ALID WIND DIRECTION-WIND SPEED-STABILITY CLASS A 1259 TOTAL HOURS CALH 0 ALL COLUHNS AND CALH TOTAL 100 PERCENT OF JOINT VALID OBSERVATIONS HETEOROLOGICAL FACILITY: LOCATED ABOUT 1.3 KH SW OF BROWNS FERRY NUCLEAR PLANT STABILITY BASED ON LAPSE RATE HEASURED BETWEEN 10.03 AHD.45.30 HETERS WIHD SPEED AHD DIRECTION HEASURED AT THE 10.42 HETER LEVFL MEAN WIND SPEED = 6.8 HPH

TABLE 1.3 (Sheet 2 of 22) 30IHT PERCENTAGE FRE UEHCIES OF WIND SPEED BY WIND DIRECTION FOR STMILITY CLASS 8 (-1-9 < DELTA-T< -1.7'C/100 M) BROWNS FERRY NUCLEAR PLANT JAN 1, 77 OEC 31, I9 WIND WINO SPEED (MPH) DIRECTION 0.6-1.4 1.5-3.4 3. 5-5. 4 5. 5-7. 4 7. 5-12. 4 32.5-18.4 18.5-24.4 >=24.5 TOTAL NN 0.0 0.0 0.05 0 09 F 0.30 0.04 0.01 0.0 0.49 HHE 0.0 0.0 0.05 0.07 0.27 0.05 0.0 0.0 0,44 HE 0.0 0.0 0.04 0.02 0.09 0.01 0.0 0.0 0.16 EHE 0.0 0.01 0.01 0.01 0.01 0.0 0.0 0.0 0.04 E 0.0 0.0 0.02 0.01 0.0 0.0 0.0 0.0 0.03 ESE 0.0 0.02 0.10 0.04 0.0 0.0 0.0 0.0 0.16 SE 0.0 0.13 0.64 0.09 0.02 0.0 0.0 0.0 0.88 SSE 0.0 0.09 0.31 0.02 0.01 0.0 0.0 0.0 0'. 43 S 0.0 0.05 0.42 0.07 0.02 0.0 , 0.0 0.0 0. 56 SSW 0.0 0.02 0.07 0.01 0.0 0.0 0.0 0.0 0.10 SW 0.0 0.0 0.17 0.02 0.0 0.0 0.0 0.0 0.19 WSW 0.0 0.0 0.11 0.13 0.05 0.01 0.0 0.0 0.30 W 0.0 0.02 0.04 0.17 0.17 0.03 0.0 0.0 0.43 WNW 0.0 0.0 0.07 0.11 0.23 0.08 0.04, 0.0 0.53 HW 0.0 0.0 0.01 0.07 0.27 0.13 0.01 0.0 0.49 HNW 0.0 0.0 0.0 0.07 0.19 0.12 0.0 0.0 0.38 SUBTOTAL 0.0 0.34 2.11 1.00 1.63 0.47 0.06 0.0 5.61 TOTAL HOURS OF VALID STABILITY OBSERVATIONS 25935 TOTAL HOURS OF STABILITY CLASS B 1445 TOTAL HOURS OF VALID WINO DIRECTION-WIND SPEED-STABILITY CLASS B 1440 TOTAL HOURS CALM 0 ALL COLUMNS AHD CALM TOTAL 100 PERCENT OF JOINT VALID OBSERVATIONS I METEOROLOGICAL FACILITY;METEOROLOGICAL FACILITY LOCATEO 1.3 KM ESE OF BROWHS FERRY NUCLEAR PLANT i'll'khgo'Qh'DIERN'hh PQUS'hP'O'I'8 tt~N MlkL"'"""'EAN WIND SPEED = 7.2 MPH

) ~

TABl.E 1.3 (Sheet 3 of 22) JOINT PERCENTAGE FRE UENCIES OF WINO SPEED BY WIND DIRECTION FOR ST+ILITY CLASS C (-1.7 < DELTA-T< -1.5'C/100 ll) BROMHS FERRY NUCLEAR PLANT JAN 1, 77 DEC 31, 79 WIHD WIND SPEED (MPH) OI RECT ION 0. 6-1 .4 1. 5-3. 4 3. 5-5. 4 5. 5-7. 4 7 ~ 5-12-4 12. 5-18.4 18. 5-24.4. >=24. 5 TOTAL 0.0 0.01 0.08 0.11 0. 21 0.02 0.0 0.0 0.43 HNE 0.0 0.01 0.07 0.09 0.17 0.20 0.0 0.0 0.36 HE 0.0 0.0 0.03 0.08 0.05 0.0 0.0 0.0 0.16 EHE 0.0 0.0 0.02 0.02 0.0 0.0 0.0 0.0 0.04 E 0.0 0.0 0.03 0.02 0.0 0.0 0.0 0,0 0.05 ESE 0.0 0.01 0.05 0.02 0.0 0.0 0.0 0.0 0.08 SE 0,0 0.17 0.29 0.09 0.01 0.0 0.0 0.0 0.56 SSE 0.0 0.12 0.17 0.04 0.01 0.0 0.0 0.0 0.34 S 0.0 0.11 0.25 0.04 0.02 0.0 ',.0.0 0.0 0.42 SSW 0.0 0.03 0.06 0.01 . 0.0 0.0 0.0 0.0 0.10 SW 0.0 0.03 0.12 0.03 0.01 0.0 0.0 0 0

                                                                                                            ~       0;19 WSW            0.0             0.0           0.11      0.07           0.07          0.0         0.0        0,0       0.25 W              0.0             0.0           0.05      0.12           0.10          0.02        0.01       0.0       0.30 WNW            0.0             0.01          0.12      0.13           0.17          0.07        0.04       0.0       0.54 NW             0.0             0.0          .0.05      0.09           0.22          0.10        0.01       0.0       0.47 NNW            0.0             0.0           0.02      0.08           0.18          0.10        0.0        0.0       0.38 SUBTOTAL        0.0            0.50          1.52      1.04           1.22          0.33        0.06       0.0       4.67 TOTAL   HOURS OF   VALID STABILITY OBSERVATIONS                                       25935 TOTAL   HOURS OF   STABILITY CLASS     C                                               1202 TOTAL   HOURS OF VALID WIND      DIRECTION-WIND SPEED-STABILITY CLASS          C       1197 TOTAL   HOURS CALM                                                                        0 ALL COLUHHS AHD CALH TOTAL 100 PERCENT OF JOINT VALID OBSERVATIONS HETEOROLOGICAL FACILITY:l1ETEOROLOGICAL FACILITY LOCATED 1.3 KH ESE OF BROlJNS FERRY NUCL'EAR PLANT STABILITY BASED OH LAPSE RATE HEASUREO BETWEEN 10.03 AHD 45.30 HETERS WIHD SPEED ANO DIRECTION HEASURED AT THE'(10.42 l1ETER l.EVEL HEAH WIND SPEED =       7.0  HPH
                                                                                                                         ~pl y I

TABLE 1.3 (Sheet 4 of 22) DOIHT PERCENTAGE FRE UENCIES OF WIND SPEED BY WIND DIRECTION FOR STABILITY CLASS D (-1.5 < DELTA-T< -0.5'C/100 M) BROWNS FERRY NUCLEAR PLANT DAH 1, 77 DEC 31, 79 WIND WIND SPEED (MPH) DIRECTION 0.6-1.4 1.5-3.4 3.5-5.4 5.5-7.4 7.5-12.4 12.5-18.4 18.5-24.4 )=24.5 TOTAL H 0.0 0.19 0.41 0.53 1.00 0.37 0.01 0.0 2.51 NHE 0.01 0.20 0.56 0.58 1.18 0.18 0.01 0.0 2.72 NE 0.01 0.12 0.38 0.43 0.52 0.01 0.0 0.0 1.47 fHE 0,0 0.26 0.23 0.15 0.05 0.01 0.0 0.0 0.70 E 0.0 0.20 0.31 0.17 0.05 0.0 0.0 0.0 0.73 ESE 0.0 0.24 0.51 0'. 30 0.08 0.0 0.0 0.0 1.13 SE 0.02 1.16 1.31 0.83 0.26 0.0 0.0 0.0 3.58 SSE 0.01 0.99 0.99 0.26 0.11 0.02 0.0 0.0 2:38 S 0.0 0.92 1.17 0.34 0.17 0.0 0.0

                                                                                          '.0        0.0       2 '0 SSW            0.0          0.45        0.29     0.08           0.04           0.0                    0.0       0.86 SW             0.0           0.24       0.29     0.09           0.02           0 Ol
                                                                                ~          0.0       0.0       0.65 WSW            0.0          0.32        0.70     0.29           0.33           0.11         0.0       0.0       1.75 W              0.0           0.18       0.55     0.62            0.63          0.22         0.03      0.0       2.23 WHW            0.0           0.13       0.39     0.42            1.10          0.82         0.22      0.01      3.09 NW             0.0           0.04       0.28     0.38            1.01          0.87         0.14      0.02      2.74 HNW            0.0           0.13       0.40     0.55            1.54          0.74         0;05  ~   0.0       3.41 SUBTOTAL       0.05          5.77       8.77     6.02            8.09          3.36          0.46     0.03. 32.55 TOTAL   HOURS OF  VALID STABILITY OBSERVATIONS                                   25935 TOTAL   HOURS OF STABILITY CLASS D                                                 8438 TOTAL   HOURS OF VALID WIND DIRECTION-WIND   SPEED-STABILITY CLASS        D        8341 TOTAL   HOURS CALM                                         ~

1 ALL COLUMNS AND CALM TOTAL 100 PERCENT OF JOINT VALID OBSERVATIONS l METEOROLOGICAL FACILITY:METfOROLOGICALFACILITY LOCATED,1.3 KM fSf OF BROWNS FERRY NUCLEAR PLANT BAQB 30 HETERS PI(Ill)gf NEHtm KhUINllS@E)UFItl93 INTN LINE4L5 g, J I MEAN WIND SPEED = 7.1 MPH 4 At

                                                                                                                    'U,A ~

TABI.E 1.3 (Sheet 5 of 22) 30IHT PERCENTAGE FRE UEHCIES OF WIND SPEED BY WINO DIRECTION FOR STABILITY CLASS E (-0.5 < DELTA-T< 1.5'C/100 M) BROHHS FERRY NUCLEAR PLAIIT DAH 1, 77 OEC 31, 79 HI HO WIND SPEED (MPII) DIRECTION 0.6-1.4 1.5-3.4 3.5-5.4 5.5-7.4 7.5-12.4 12.5-18.4 18.5-24.4 >=24 5 TOTAL H 0.04 0.47 0.54 0.43 0.41 0.05 0.01 0.0 1.95 t)HE 0.05 0.61 0.74 0.55 0.47 0.04 0.0 0.0 2.46 HE 0.05 0.57 0.63 0.42 0.27 0.02 0.0 0.0 1.96 EHE 0.05 0.71 0.45 0.17 0.08 0.02 0.0 0.0 1.48 E 0.04 0.61 0.74 0.16 0.07 0.0 0.0 0.0 1.62 ESE 0.03 0.76 1.01 0.53 0.16 0.01 0.0 0.0 2.50 SE 0.1'1 2.04 1.75 0.92 0.55 0.02 0.0 0.0 5.39 SSE 0. 07 1.16 0.78 0.48 0.33 0.04 0.0 0.0 2;86 S 0.05 1.03 0.74 0.44 0.63 0.14 ~ 0.01 0.0 3.04 SSH 0.02 0.52 0.14 0.08 0.06 0.01 0.0 0.0 0.83 SW 0.04 0.30 0.07 0.02 0.03 0.0 0.0 0.0 0.46 WSH 0.01 0.53 0.60 0.14 0.11 0.04 0.0 0.0 1.43 W 0.02 0.37 0.77 0.42 0.27 0.04 0.0 0.0 1.89 HNH 0.03 0.15 0.13 0.11 0.22 0.09 0.02 0.0 0.75 HH 0.02 0.17 0.20 0.14 0.25 0.09 0.02 0.0 0.89 NHH 0.05 0.41 0.48 0. 54 0.59 0,09 .0.01 ~ 0.0 2.17 SUBTOTAL 0.68 10.41 9.77 5.55 4.50 0.70 0.07 0.0 31. 68 TOTAL HOURS OF VALID STABILITY OBSERVATIONS 25935 TOTAL IIOURS OF STABILITY CLASS E 8264 TOTAL HOURS OF VALID WINO DIRECTION-HIND. SPEED-STABILITY CLASS E 8098 TOTAL HOURS CALM 3 ALL COLUMNS AHD CALM TOTAL 100 PERCENT OF JOINT VALID OBSERVATIONS I I gjgl)gIDDAAQDDQEHIQt (QDNIS)lfEI [EJECT III'I METEOROLOGICAL FACILITY:METEOROLOGICAL FACILITY LOCATEO 1'.'3 KM ESE OF BROHNS FERRY NUCLEAR PLANT 45.30 IIETEIIs MEAN WINO SPEED = 5.0 MPII I'

E~

I'

TABLE 1.3 (Sheet 6 of 22) JOINT PERCENTAGE FRE UENCIES OF WIND SPEED BY WIND DIRECTION FOR SALABILITY CLASS F (1.5 < DELTA-T< 4.0'C/100 M) BROWHS FERRY NUCLEAR PLANT DAH 1, 77 DEC 31, 79 WIND WIND SPEED (MPH) DIRECTION 0.6-1.4 1.5-3.4 3.5-5.4 5.5-7.4 7.5-12.4 12.5-18.4 18.5-24.4. >=24.5 TOTAL 0.05 0.36 0. 52 0.28 0.06 0.0 0.0 0.0 1.27 HHE 0.05 0.51 0.66 0 '4 0.11 0.0 0.0 0.0 1.67 HE 0.07 0.34 0.27 0.18 0.01 0.0 0.0 0.0 0.87 EHE 0.03 0.53 0.33 0.05 0.0 0.0 0.0 0.0 0.94 E 0.01 0 '9 0.52 0.03 0.0 0.0 0.0 0.0 1.15 ESE 0.0 0.52 0.22 0.0 0.0 0.0 0.0 0.0 0.74 SE 0.09 0.97 0.48 0.17 0.13 0.01 0.0 0.0 1.85 SSE 0.05 0.54 0.34 0.17 0.25 0.02 0.01 0.0 1.38 S 0.03 0.29 0.18 0.20 0.27 0.01 ', 0.0 0.0 0.98 SSW 0.03 0.13 0.03 0.0 0.01 0.0 0.0 0.0 0.20 SW 0.0 0.09 0.03 0.0 0 0 0.0 0.0 0.0 0:12 WSW 0.0 0.09 0.07 0.0 0.0 0.0 0.0 0.0 0.16 W 0.02 0.09 0.06 0.0 0.01 0.0 0.0 0.0 0.18 WNW 0.01 0.08 0.01 0.0 0.0 0.0 0.0 0.0 0.10 HW 0.01 0.08 0.04 0.01 0.0 0.0 0.0 0.0 0.14 HHW 0.05 0.27, 0.27 0.16 0.05 0.0 0.0 0.0 0.80 SUBTOTAL 0.50 5.48 4.03 1.59 0.90 0.04 0.01 0.0 12.55 TOTAL HOURS OF VALID STABILITY OBSERVATIONS 25935 T01AL HOURS OF STABILITY CLASS F 3268 . TOTAL HOURS Of VALID WIND DIRECTION-WIND SPEED-STABILITY CLASS F 3223 TOTAL HOURS CALM 4 ALL COLUMNS AND CALM TOTAL 100 PERCENT OF JOINT VALID OBSERVATIONS 4 METEOROLOGICAL FACILITY:METEOROLOGICAL FACILITY LOCATED 1.3 KM ESE OF BROWNS FERRY NUCLEAR PLANT HETEBS ffgllgPBBA@BBIEHlfQ gQ JQSIIltEljigEj(Ej) QT(i] tg)E45.30

                                                                                                                           ~ "i MEAN WIND SPEED  =  4.0 MPH                                                                              ~ i       4 g
                                                                                                                 ~

qI'5:

                                                                                                                    >z.l n

TABLE 1.3 (Sheet 7 oI'2) JOINT PfRCENTAGE FRE UEHCIES OF WIND SPEED BY WIND DIRECTION FOR p STABILITY CLASS G (DELTA-T> 4.0'C/100 H) BROWNS FfRRY NUCLEAR PLANT JAN 1, 77 DEC 31, 79 WIND WIND SPEED (HPII) DIRECTION 0.6-1.4 1.5-3.4 3.5-5.4 5. 5-7.4 7. 5-12.4 12. 5-18. 4 18. 5-24 ~ 4 >=24.5 TOTAL H 0.07 0.76 0.32 0.02 0.0 0.0 0.0 0.0 1.17 NHE 0.05 0.83 0.51 0.18 0.02 0.0 0.0 0.0 1. 59 HE 0.04 0.34 0.12 0.02 0.0 0.0 0.0 0.0 0.52 EHE 0.04 0.48 0.18 0.02 0.0 0.0 0.0 0.0 0.72 E 0.02 0.52 0.34 0.0 0.0 0.0 0.0 0.0 0.88 ESE 0.01 0.18 0.01 ." 0.0 0.0 0.0 0.0 0.0 0.20 SE 0.08 0.43 0.09 0.04 0.03 0.0 0.0 0.0 0.67 SSE 0.03 0.44 0.31 0.16 0.08 0.0 0.0 0.0 1.02 S 0.05 0.09 0.12 0.10 0.04 0.0 ',.0.0 0.0 0.40 SSW 0.05 0.05 0.01 0.0 0.0 0.0 0.0 0.0 0.11 SW 0.0 0.01 0.0 0.0 0.0 0.0 0.0 0.0 0.01 WSW 0.02 0.02 0.0 0.0 0.0 0.0 0.0 0.0 0.04 W 0.01 0.01 0.0 0.0 0,0 0.0 0.0 0.0 0.02 WHW 0.01 0.02 0.0 0.0 0.0 0.0 0.0 0.0 0.03 HW 0.04 0.04 0.0 0.0 0.0 0.0 0.0 0.0 0.08 HHW 0.05 0.23, 0.12 0.03 0.0 0.0 0.0 0.0 0.43 SUBTOTAL 0.57 4.45 2.13 0.57 0.17 0.0 0.0 0.0 7.89 TOTAL HOURS OF VALID STABILITY OBSERVATIONS 25935 TOTAL IIOUIIS OF STABILITY CLASS G 2056 TOTAL IIOURS OF VALID WIND DIRECTION-WIND SPEED-STABILITY CLASS G 2019 TOTAL IIOURS CALH 4 ALL COI.UHHS AND CALH TOTAL 100 PfRCEHT OF JOINT VALID OBSfRVATIOHS I HETEOROLOGICAL FACILITY:HETEOROLOGICAL FACILITY LOCATED 1.3 KH ESE OF DROWNS FERRY NUCLEAR PLANT HEAH WIND SPfED = 3.2 HPH ~ ~ st '

                                                                                                                        <<.'i ~

TABLE 1.3 (Sheet 8 of 22) JOINT PERCENTAGE FRE UEHCIES OF WIND SPEED BY WIND DIRECTION h I DISREGARDING STABILITY CLASS BROWHS FERRY NUCLEAR PLANT JAH 1, 77 DEC 31, 79 WIND WIND SPEED (MPII) 8IOECTIOH O. 6-1.4 1. 5-3.4 3. 5-5.4 5.5-7.4 7. 5-1 2.4 12. 5-1 8.4 18. 5-24.4 >=24. 5 TOTAL N 0.02 0.19 0.38 0.64 2.07 2.47 0.61 0.06 6.44 HHE 0.0 0.13 0.33 0.60 2.46 2.69 0.50 0.04 6.75 HE 0.0 0.12 0.35 0.64 2.16 1.85 0.58 0.02 5.72 EHE 0.02 0.14 0.32 0.36 1.15 0.95 0.34 0.04 3.32 E 0.0 0.22 0.47 0.45 0.99 0.43 0.08 0.01 2.65 ESE 0.01 0.23 0.53 0.66 1.79 1.63 0.42 0.09 5.36 SE 0.02 0.36 1.26 1.36 3.25 3.20 1.,54 0.69 11.68 SSE 0.01 0.38 1.20 1.22 2.97 2.59 1.16 0.59 10.12 S 0.02 0.40 0.90 1.05 2.53 2.40 1.03 0.43 8.76 SSW 0.0 0.31 0.65 0.69 1.73 1.77 0.73 0.19 6:07 SW 0.02 0.38 0.66 0.69 1.55 1.62 0.50 0.14 5.56 WSW 0.01 0.26 0.69 0.68 1.15 1.05 0.36 0.17 4.37 W 0.02 0.20 0.66 0.81 1.76 1.04 0.42 0.35 5.26 WNW 0.01 0.17 0.46 0.69 2.03 1.54 '.76 0.30 5.96 HW 0.02 0.19 . 0.49 0.70 1.80 2.01 0.96 0.28 6.45 NHW 0.01 0.22 0.28 0.41 1.66 2.13 '.70 0.13 5.54 SUBTOTAL 0.19 3.90 9.63 11.65 '1.05 29.37 10 69 3 53 100,01 TOTAL HOURS OF VALID WIND OBSERVATIONS 25784 TOTAL HOURS OF OBSERVATIONS 26280 RECOVERABILITY PERCENTAGE 98.1 TOTAL HOURS CALH 2 ALL COLUMNS ANO CALH TOTAL 100 PERCENT OF JOINT VALID OBSERVATIONS I I HETEOROLOGICAL FACILITY:HETEOROLOGICAL FACILITY LOCATED 1.3 KH ESE OF BROWHS FERRY NUCLEAR PLANT WIND SPEED AHD DIRECTION HEASURED AT THE)92.63 HETER LEVEL HEAN WIND SPEED = 12.0 HPH

TABLE 1.3 (Sheet 9 of 22) 3OIHT PERCENTAGE FRE UEHCIES OF WIND SPEED BY WIND DIRECTION FOR STABILITY CLASS A (DELTA-T< -1.9'C/100 H) BROWHS FERRY NUCLEAR PLANT PART 1 OF 2 GROUND LEVEL RELEASE HOnE JAN 1, 77 DEC 31, 79 WIND WIND SPEED (MPH) DIRECTION CALM 0.6-1.4 1.5-3.4 3.5-5.4 5.5-7.4 7.5-12 .4 12.5-18.4 18.5-24.4 >=24:5 TOTAL N 0.0 0.0 0.0 0.0 0.0 0.02 0.01 0.0 0.0 0.03 HHE 0.0 0.0 0.0 0.0 0.0 0.03 0.02 0.0 0.0 0.05 NE 0.0 0.0 0.0 0.0 0.0 0.01 0.0 0.0 0.0 0.01 ENE 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 E 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 ESE 0.0 0.0 0.0 0.0 0.02 0.0 0.0 0.0 0.0 0.02 SE 0.0 0.0 0.0 0.05 0.04 0.01 0.0 0 .,0 0.0 0.10 . SSE 0.0 0.0 0.0 0.03 0.02 0.01 0.0 0.0 0.0 0.06 S 0.0 0.0 0.0 0.02 0.02 0.01 0.0 0.0 0.0 0.05 SSW 0.0 0.0 0.0 0.0 0.01 0.0 0.0 0.0 0.0 0.01 ~ SW 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 WSW 0 0

              ~        0.0       0.0       0.0       0.01        0 01 F           0.0          0.0     0.0    0.02 W             0.0       0.0       0.0       0.0       0.0         0.01          0.0          0.0 . 0.0    0.01 WHW           0.0       0.0       0.0       0.0       0.0         0.01          0.01         0.0     0.0    0.02 HW            0.0       0.0      ,0. 0      0.0       0.0         0.02          0.02         0.0 ~   0.0    0.04 NHW           0.0       0.0       0.0       0.0       0.0         0.01          0.02         0 . 02  0.0    0.05 SUBTOTAL      0.0       0.0       0.0       0.10      0.12        0.15        - 0.08         0.02    0.0    0.47 TOTAL   HOURS OF VALID OBSERVATIONS                                              25482.0 TOTAL   HOURS OF GROUND LEVEL RELEASE                                              2832.4 TOTAL   HOURS OF STABILITY CLASS A                                                  133.1 TOTAL   HOURS OF GROUND LEVEL  STABILITY CLASS    A                                 127,5 HETEOROLOGICAL    FACILITY: HETEOROLOGICAL FACILITY LOCATED 1.3         KH ESE OF BROWNS FERRY NUCLEAR PLANT STABILITY BASED    OH DELTA-T BETWEEN 10.03 AHD 45.30 I'IETERS
                                                                                    ~ %

WIND DIRECTION HEASURED AT 10.42 HETER LEVEL I

TABLE 1.3 (Sheet 10 of 22) SPLIT JOINT PERCENTAGE FRE UEHCIES OF WINO SPEED BY WIND DIRECTION FOR STABILITY CLASS 8 (-1.9 < Delta T < -1.7'/100H) BROWHS FERRY NUCLEAR PLAHl PART 1 OF 2 GROUND LEVEL RELEASE MODE DAH 1, 77 DEC 31, I9 WIND WINO SPEED (MPH) OIRECTIOM CALM 0.6-1.4 1.5-3.4 3.5-5.4 5.5-7.4 7.5-12.4 12.5-18.4 18.5-24.4 >=24:5 TOTAL H 0.0 0.0 0.0 0.0 0.01 0.05 0.01 0.01 0' 0.08 NHE 0.0 0.0 0.0 0.0 0.01 0 '5 0.01 0.0 0.0 0.07 HE 0.0 0.0 0.0 0.0 0.0 0.01 0.0 0.0 0.0 0.01 EHE 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 E ESE 0.0 0.0 0.0 0.0 '.01 0.0 0.0 0.0 0' 0.01. SE 0.0 0.0 0.0 0.02 0.02 0.01 0.0 0;0 0.0 0.05-SSE 0.0 0.0 0.0 0.01 0.01 0.0 0.0 " 0.0 0.0 0.02 S 0.0 0.0 0.0 0.02 0.01 0.01 0.0 0.0 0.0 0.04 SSW 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 SW 0,0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 WSW 0.0 0.0 0.0 0.0 0.02 0.01 0.0 . 0.0 0.0 0.03 W 0.0 0.0 0.0 0.0 0.01 0.02 0.02 0.01 0.0 0.06 WHW 0.0 0.0 0.0 0.0 0.01 0.03 0.02 '.03 0.0 0.09 HW 0.0 0.0 ,0. 0 0.0 0.01 0.04 0.03 0.0 0.0 0.08 NNW 0.0 '.0 0.0 0.0 0.0 0.03 0.04 0.0 0.0 0.07 SUBTOTAL 0.0 0.0 0.0 0.05 0.12 0.26 ~ 0.13 0.05 0.0 0.61 , TOTAL HOURS OF VALID OBSERVATIONS 25482.0

'lOTAL HOURS OF GROUND LEVEL RELEASE                                            2832.4 TOTAL HOURS OF STABILITY CLASS 8 185.1'63.4 TOTAL HOURS OF GROUND LEVEL STABILITY CLASS 8 HETEOROLOGICAL FACILITY:FIETEOROLOGICAL FACILITY LOCATED-'1.3 KN ESE OF BROWNS FERRY NUCLEAR PLANT STABILITY BASED OH DELTA-T BETWEEN 10.03 AHD 45.30 HETERS WIND DIRECTION HEASUREO AT 10.42 HETER LEVEL

'@PE@PEP QHICPEO $$ Q.I)P5METER LEVELI

TABLE 1.3 (Sheet ll of 22) SPLIT JOINT PERCENTAGE FRE UENCIES OF WIND SPEED BY WIND DIRECTION FOR STABILITY CLASS C (-1.7 < DELTA-T< -1.5'C/100 M) BROWHS FERRY NUCLEAR PLANT PART 1 OF 2 GROUND LEVEL RfLEASE MODE JAH 1, 77 OEC 31, 79 WIND WIND SPEED (MPH) DIRECTION CALM 0.6-1.4 1 ~ 5-3.4 3.5-5.4 5.5-7.4 7.5-12.4 12.5-18.4 18. 5-24. 4 >=24. 5 TOTAL H 0.0 0.0 0.0 0.0 0.01 0.03 0,0 0.0 0.0 0.04 HHE 0.0 0.0 0.0 0.0 0.01 0.02 0.0 0.0 0.0 0.03 HE 0.0 0.0 0.0 0.0 0.01 0.01 0.0 0.0 0.0 0.02 ENE 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 E 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 ESE 0.0 0.0 0.0 0.0, 0.0 0.0 0.0 0.0 0.0 0.0 SE . 0.0 0.0 0.0 0.01 0.01 0.0 0.0 0.0 0.0 0.02 -.. SSE 0.0 0.0 0.0 0.01 0.01 0.01 0.0 ~ 0.'0 0.0 0.03 S 0.0 0.0 0.0 0.01 0.01 0.01 0.0 0.0 0.0 0.03 SSW 0.0 0.0 0.0 0.0 0.0 0.0- 0.0 0.0 0.0 0.0 SW 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 WSW 0.0 0.0 0.0 0.0 0.01 0.01 0.0 0.0 0.0 0.02 W 0.0 0.0 0.0 0.0 0.01 0.01 0. 01'.02 0.01 0.0 0.04 WNW 0.0 0.0 0.0 0.0 0.01 0,02 0.03 0.0 0.08 HW 0.0 0.0 0.0 0.0 0.01 0.03 0.02 0.01 ~ 0.0 0.07 HNW 0.0 0.0 '0. 0 0.0 0.01 0.02 0.03 0.0 0.0 0.06 SUBTOTAL 0.0 0.0 0.0 0.03 0.11 0.17 . . 0.08 0.05 0.0 0.44 TOTAL HOURS OF VALID OBSERVATIONS 25482.0 TOTAL HOURS OF GROUND LEVEL RELEASE 2832.4 TOTAL HOURS OF STABILITY CLASS C 259.0, TOTAL HOURS OF GROUND LEVEL STABILITY CLASS C 106.3 METEOROLOGICAL FACILITY:METEOROLOGICAL FACILITY LOCATED 1.3 KM ESf OF BROWNS FERRY NUCLEAR PLANT STABILITY BASED OH DEL1'A-T BETWEEN '10.03 AND 45.30 METERS WIND DIRECTION MEASURED AT 10.42 METER'LEVEL EFFLUfHT VELOCITY = 12.60 M/S

TABLE 1.3 (Sheet 12 of 22) SPLIT JOINT PERCENTAGE FRE UEHCIES OF WIND SPEED BY WINO DIRECTION FOR S'ABILITY CLASS D (-1.5 < DELTA-T< -0.5'C/100 H) FERRY NUCLEAR PLANT 'ROWNS PART 1 OF 2 GROUND LEVEL RELEASE NODE JAN 1, 77 DEC 31, 79 WIND WIND SPEED (MPH) DIRECTION CALM 0.6-1.4 1.5-3.4 3.5-5.4 5.5-7.4 7.5-12.4 12.5-18.4 18.5-24.4 >=24.5 TOTAL H 0.0 0.0 0.0 0.01 0.04 0.15 0.10 0.01 0.0 0.31 HHE 0.0 0.0 0.0 0.01 0.05 0.18 0.05 0.01 0.0 0.30 HE 0.0 0.0 0.0 0.01 0.04 0.08 0.0 0.0 ~ 0.0 0.13 EHE 0.0 0.0 0.0 0.01 " 0.01 0.01 0.0 0.0 0.0 0.03 E 0.0 0.0 0.0 0.01 0.02 0.01 0.0 0.0 0.0 0.04 ESE 0:0 0.0 0.0 0.03 0.04 0.01 0.0 0.0 0.0 0.08 SE 0.0 0.0 0.01 0.11 0.13 0.06 0.0 0.0 0.0 0.31 . SSE 0.0 0.0 0.02 0.09 0.06 0.05 0.02 ',. 0.0 0.0 0.24 S 0.0 0.0 0.02 0.09 0.06 0.06 0.0 . 0.0 0.0 0.23 SSW 0.0 0.0 0.01 0.02 0.01 0.01 0.0 0.0 0.0 0.05 SW 0.0 0.0 0.0 0.01 0.01 0.0 0.01 0.0 0.0 0.03 WSW 0.0 0.0 0.0 0.03 0.03 0.06 0.04 0.0 0.0 0.16 W 0.0 0.0 0.0 0.02 0.06 0.10 0.09 0.02, 0,0 0.29 WNW 0.0 0.0 0.0 0.0 0.03 0.16 0.19 0.14 0.01 0.53 HW 0.0 0.0 ,0. 0 0.0 0.03 0.15 0.23 0.10 ~ 0.02 0.53 HNW 0.0 0.0 0.0 0.01 0.05 0.25 0.19 0.04 0.0 0.54 SUBTOTAL 0.0 0.0 0.6 0.46 0.67 1.34 '.92 0.32 0.03 3.80 TOTAL HOURS OF VALID OBSERVATIONS 25482.0 TOTAL HOURS OF GROUND LEVEL RELEASE 2832.4 TOTAL HOURS OF STABILITY CLASS D 13904.'1 ~ TOTAL HOURS OF GROUND LEVEL STABILITY CLASS D 968.6' HETEOROLOGICAL FACILITY:METEOROLOGICAL fACILITY LOCATED.1.3 KH ESE OF BROWNS FERRY NUCLEAR'PLAHT STABILITY BASED OH DELTA-T BETWEEN 10.03 AND 45.30 METERS WIND DIRECTION HEASURED AT 10.42 HETER'LEVEL EFFLUENT VELOCITY = 12.60 H/S 4

                                                                                                                    ~ ~
                                                                                                                          ,4r

TABLE 1.3 (Sheet 13 of 22) SPLIT JOINT PERCENTAGE FRE UENCIES OF HIND SPEED BY HIND DIRECTION FOR

                                   ,STABILITY CLASS  E    (-0.5<DELTA-T< 1.5'C/100                     M)

BRONHS FERRY NUCLEAR PLANT PART 1 OF 2 GROUND LEVEL RELEASE MODE DAH 1, 77 DEC 31, 79 WIND HIND SPEED (MPH) DI RECT I OH CALM 0.6-1.4 1.5-3.4 3.5-5.4 5.5-7.4 7.5-12.4 12.5-18.4 18.5-24.4 >=24.5 TOTAL H 0.0 0.0 0.0 0.04 0.06 0.07 0.02 0.01 0.0 0.20 HNE 0.0 0.0 0.01 0.06 0.07 0.08 0.02 0.0 0.0 0.24 HE 0.0 0.0 0.01 0.06 0.06 0.05 0.01 0.0 0.0 0.19 ENE 0.0 0.0 0.02 0.04 0.03 0.01 0.01 0.0 0.0 0.11 E 0.0 0.0 0.02 0.07 0.02 0.01 0.0 0.0 0.0 0.12 ESE 0.0 0.0 0.02 0.08 0.07 0.03 0.0 0.0 0.0 0.20 SE 0.0 0.0 0.08 0.22 0.16 0.18 0.02 0.0 0.0 0.66 SSE 0.0 0.0 0.05 0.12 0.12 0.19 0.04 0.0 0' 0.52 S 0.0 0.0 0.06 0.10 0.09 0.27 0.13 0.01 0.0 0.66 SSH 0.0 0.0 0.02 0.02 0.02 0.02 0.01 0.0 0' 0.09 SH 0.0 0.0 0.01 0.0 0.0 0.01 0.0 0.0 0.0 0.02 NSH 0.0 0.0 0.01. 0.05 0.02 0.03 0.02 0.0 0.0 0.13 W 0.0 0.0 0.01 0.06 0.05 0.05 0.01 0.0, 0.0 0.18 NHW 0.0 0.0 0.0 0.01 0.01 0.04 0.02 0.01 0.0 0.09 HH 0.0 0.0 0.0 0.01 0.02 0.04 0.03 0.01 ~ 0.0 0.11 NNM 0.0 0.0 0.0 0.03 0.07 0.10 0.02 0.01 0.0 0.23 SUBTOTAL 0.0 0.0 0.32 0.97 0.87 1.18 ~ 0.36 0.05 0.0 3.75 TOTAL HOURS OF VALID OBSERVATIONS 25482.0 TOTAL HOURS OF GROUND LEVEL RELEASE 2832.4 TOTAL HOURS OF STABILITY CLASS E 7920:6 TOTAL HOURS OF GROUND LEVEL STABILITY CLASS E 957.9'ETEOROLOGICAL FACILITY:METEOROLOGICAL'FACILITY LOCATED'1.3 KM ESE OF BROWNS FERRY NUCLEAR'PLANT STABILITY BASED OH DELTA-TBETNEEH 10.03 AND 45.30 METERS WIND DIRECTION MEASURED AT THE 10.42 METER LEVEL 8FPuB'f'llvL%BH'l 8 48 A)s"'"" "'"'4

                                                                                                                             ~ ~
                                                                                                             ~"

TABLE 1.3 (Sheet 14 of 22) SPLIT JOINT PERCENTAGE FRf UEHCIES OF WIND SPfED BY WIND DIRFCTIOH FOR STABILITY CLASS F (1.5 < DfLTA-T< 4.0'C/100 H) PART 1 OF 2 GROUND LEVEL RELEASE NODE BROWHS FERRY NUCLEAR PLAN1'AH 1, *77 DEC 31, 79 WIND WIND SPf ED (MPH) DIRECTION CALM 0.6-1.4 1.5-3.4 3. 5-5.4 5. 5-7.4 7. 5-1 2.4 12.5-18.4 18.5-24.4 >=24.5 TOTAL H 0.0 0.0 0.01 0.06 0.04 0.01 0.0 0.0 0.0 0.12 HNE 0.0 0.0 0.01 0.08 0.05 0.02 0.0 0.0 0.0 0.16 NE 0.0 0.0 0.01 0.03 0.03 0.0 0.0 0.0 0.0 0.07 EHE 0.0 0.0 0.02 0.03" 0.01 0.0 0.0 0.0 0.0 0.06 E 0.0 0.0 0.01 0.04 0.0 0.0 0.0 0.0.- 0.0 0.05 ESE 0.0 0.0 0.02 0.02 0.0 0.0 0.0 0.0 0.0 0.04 SE 0.0 0.0 0.05 0.06 0.03 0.06 0.01 0.0 0.0 0.21 SSE 0.0 0.0 0.04 0.06 0.05 0.18 0,02 0.01 0.0 0.36 . S 0.0 0.0 0.02 0.03 0.04 0.11 0.01 0.0 0.0 0.21 SS1J 0.0 0.0 0.01 0.0 0.0 0.0 0.0 0.0 0.0 0.01 SW. 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 WSW 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0. 0.0 0.0 W 0.0 0.0 0.0 0.01 0.0 0.0 0.0 0.0 0.0 0.01 WHW 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 HW 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 NNW 0.0 0.0 0.01 0.03 0.02 0.01 ~ 0.0 0.0 0.0 0.07 i SUBTOTAL 0.0 0.0 0.21 0.45 0.27 0.39 0.04 0.01 0.0 1.37 TOTAL HOURS OF VALID OBSERVATIONS 25482.0 TOTAL HOURS OF GROUND LEVEL RELEASE 2832.4 TOTAL HOURS OF STABILITY CLASS F 2385.0 TOTAL HOURS OF GROUND LEVEL STABILITY CLASS F 357.0

                                                                   .4 HETEOROLOGICAL FACILITY:HETEOROLOGICAL FACILITY LOCATED 1.3 KH ESE OF BROWHS FERRY NUCLEAR PLANT gglgg Bg)        f00/IPt-I  lgTISE)   )t00)   N      45.30 HETERS EFFLUEHT VELOCITY =  12.60 H/S                                                                                    4 4  ~
                                                                                                                                    ~ 4 I

4 ~ '

TABLE 1.3 (Sheet 15 of 22) SPLIT JOINT PERCENTAGE FRE UEHCIES OF WIND SPEED BY WIND DIRfCTIOH FOR STABILITY CLASS G (DELTA-T> 4.0'C/100 M) PART 1 OF 2 GROUND LEVEL RELEASf MODE BROWHS FERRY NUCLEAR PLANl DAH 1, 77 DEC 31, 79 WIND WIND. SPEED (MPH) OIRECTIOM CALM 0. 6-1.4 1. 5-3.4 3. 5-5.4 5. 5-7.4 7. 5-12.4 12. 5-18. 4 18. 5-24.4 >=24. 5 TOTAL H 0,0 0.0 0.02 0.04 0.0 0.0 0.0 0.0 0.0 0.06 HHE 0.0 0.0 0.02 0.06 0.03 0.0 0.0 0.0 0.0 0.11 HE 0.0 0.0 0.01 0.01 0.0 0.0 0.0 0.0 0.0 0.02 EHE 0.0 0.0 0.01 0.01 . 0.0 0.0 0.0 0.0 0.0 0.02 E 0.0 0.0 0.01 0.01 0.0 0.0 0.0 0.0 0.0 0.02 ESE 0.0 0.0 0.01 0.0 0.0 0.0 0.0 0.0 0.0 0.01 SE 0.0 0.0 0.03 0.01 0.01 0.02 0.0 0.0 0.0 0.07 SSE 0.0 0.0 0.04 0.05 0.03 0.06 0.0 0.0'.0 0.0 0.1B S 0.0 0.0 0.01 0.02 0.02 0.01 0.0 0.0 0.06 SSW 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 SW 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 WSW 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 W 0.0 0.0 - 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 WHW 0.0 0.0 ,0.0 0.0 0.0 0,0 0.0 0.0 0.0 0.0 NW 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 NNlJ 0.0 0.0 0.01 0.01 0.08 0.0 0.0 0.0 0.0 0.02 SUBTOTAL 0.0 0.0 0.17 0.22 0.09 0.09 0.0 0.0 0.0 0.57 TOTAL HOURS OF VALID OBSERVATIONS 254B2.0 TOTAL HOURS OF GROND LEVEL RELEASE 2832.4 TOTAL HOURS OF STABILITY CLASS G 694.7 TOTAL HOURS OF GROUD LEVEL STABILITY CLASS G 151.7 METEOROLOGICAL FACILITY:METEOROLOGICAL FACILITY LOCATED 1.3 KM fSf OF BROWHS FERRY NUCLEAR PLANT STABILITY BASED OH LAPSE RATE MEASURED BETWEEN 10.03 AHD 45.30 METERS WIND SPEED AHD DIRECTION MEASURED AT THE 10.42 METER LEVEL 4 EFFLUENT VELOCITY = 12.60 M/S

                                                                                                                ~ ~
                                                                                                                    >gI I "I >

TABLE 1.3 (Sheet 16 of 22) SPLIT 3OIHT PERCENTAGE FRE UEHCIES OF WIND SPEED BY WIND DIRECTIOH fOR

                                          ,6TABILITY CLASS A (DELTA-T< -1.9 C/100 M)

PART 2 Of 2 ELEVATEO Rf LfASE MODE BROWNS FERRY HUCLfAR PLAH1 3AH 1, 77 DEC 31, 79 WIND WIND SPEED (MPH) DIRECTION CALM 0. 6-1 .4 1 . 5-3.4 3. 5-5.4 5. 5-7.4 7. 5-1 2.4 12. 5-18. 4 18.5-24.4 >=24;5 TOTAL N 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 HHE 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0~0 0.0 HE 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 EHE 0.0 0' 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 E 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 ESE 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 SE 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 SSE 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 S 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 SSW 0.0 0.0 0.0 0.0 0.01 0.0 0.0 0.0 0.0 0.01 SW 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 WSW 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 W 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 WNW 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 HW 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 HNW 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0 0

                                                                                                       ~     0.0 SUBTOTAL      0.0        0.0          0.0       0.0       0.01       0.0        ~ 0.0          0.0     0.0    0.0)

TOTAL HOURS OF VALID OBSERVATIONS 25482.0 TOTAL HOURS OF ELEVATED RELEASES 22649.6 TOTAL HOURS OF STABILITY CLASS A 133.1 TOTAL HOURS OF ELEVATEO STABILITY CLASS A 5.6 METEOROLOGICAL FACILITY:METEOROLOGICAL FACILITY LOCATEO 1..3 KM ESE OF BROWNS fERRY NUCLE)R PLANT STABILITY BASED ON DELTA-T BETWEEN 45.30 AND 89.60 METERS l WIND DIRECTION MfASURED AT 45.67 METER LEVEL gjIQNEI tI[PlfIED g$ Q. j7 !4ETER LEVEL !.

~ ~

TABLE 1.3 (Sheet 17 of 22) SPI.IT JOINT PERCENTAGE FRE UEHCIES OF WIND SPEED BY WIND DIRECTION FOR STABILITY CLASS B (-1.9 < DELTA-T< -1.7'C/100 II) BROWHS FERRY NUCLEAR PLANT PART 2 OF 2 ELEVATED RELEASE NODE DAN 1, 77 DEC 31, 79 WIND WIND SPEED (HPH) DIRECTIOH CALM 0. 6-1 .4 1 . 5-3.4 3. 5-5.4 5. 5-7.4 7. 5-12.4 12.5-18.4 18.5-24.4 >=24 5 TOTAL N 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 HttE 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 HE 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 EHE 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 E 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 ESE 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 SE 0.0 0.0 0.01 0.01 0.0 0.0 0.0 0.0 0.0 0.02 SSE 0.0 0.0 0.0 0.0 0' 0.0 0.0 0.0 0.0 0,0 S 0.0 0.0 0.0 0.0 0.0 0.0 0.0 '.0 0.0 0.0 SSW 0.0 0.0 0.0 0.0 0.0 0.01 0.0 0.0 0.0 0.01 SW 0.0 0.0 0.0 0.0 0.01 0.0 0.0 0.0 0.0 0.01 WSW 0.0 0.0 0.0 0.0 0.0 0.02 . 0.0 0.0 0.0 0.02 W 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 WHW 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 HW 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0,0 NHW 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 SUBTOTAL 0.0 0.0 0.01 0.01 0.01 0.03 .0.0 0.0 0.0 0,06 TOTAL HOURS OF VALID OBSERVATIONS 25482.0 TOTAL HOURS OF ELEVATED RELEASES 22649.6 TOTAL HOURS OF STABILITY CLASS 8 185.1 TOTAL HOURS OF ELEVATED STABIITY CLASS 8 21.8 lt HETEOROLOGICAL FACILITY: HETEOROLOGICAL FACILITY LOCATED l.l3 KH ESE OF BROWtIS FERRY NUCLEAR PLANT STABILITY BASED OH DELTA-T BETWEEN 45.30 AND 89.60 HETERS

                                                )EUEL g}g Jg[IlTglj ggUIlfD)tTEI5.$
                     =

IEQII EFFLUENT VELOCITY 12.60 N/S

TABLE 1.3 (Sheet 18 of 22) JOINT PERCENTAGE FRE UEHCIES OF WIND SPEED BY WIND DIRECTION fOR STABILITY ClASS C (-1.7 < DELTA-T< -1.5'C/100 H) BROWHS FERRY NUCLEAR PLANT PART 2 OF 2 ELEVATED RELEASE NODE DAN 1, 77 DEC 31, 79 WIND WIHD SPEED (MPH) 8IRECTIOR CALII O. 6-1. 4 1. 5-3. 4 3. 5-5.4 5. 5-1. 4 1. 5-12. 4 12. 5-18. 4 18. 5-24. 4 >=24: 5 TOTAL N 0.0 0.0 O.Q 0.0 O.Q 0.0 0.0 0.0 0.0 0.0 HHE 0.0 0.0 0.0 0.0 0.01 0.0 0.0 0.0 0.0 0.01 HE 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 EHE 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 E 0.0 0.0 0.0 0.0 0,0 0.0 0.0 0.0 0.0 0.0 ESE 0.0 0.0 0.0 0. 01'.05 0.01 0.01 0.0 0.0 0.0 0.03 SE 0.0 0.0 0.02 0.01 0.0 0.0 0.0; 0.0 0.08 SSE 0.0 0.0 0.0 0.04 0.0 0.0 0.0 '0.0 0.0 0.04 S 0.0 0.0 0.01 0.01 0.0 0.0 0.0 0.0 0.0 O.Q2 SSW 0.0 0.0 0.0 0.02 0.02 0.01 0.0 0.0 0.0 0.05 SM 0.0 0.0 0.0 0.05 0.05 0.02 0.01 0.0 0.0 0.13 WSM 0.0 0.0 0.0 0.0 O.Q3 0.05 0.01 0.0 0.0 0.09 M 0.0 0.0 0.0 0.0 0.01 0.03 0.02 0.02 0.0 0.08 MNM 0.0 0.0 0.0 0.0 0.0 0.02 0.02 0.0 0.0 0.04 NW 0.0 0.0 0.0 0.0 0.0 0.0 0.01 0.0 0.0 0.01 HNW 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 SUBTOTAL 0.0 0.0 0.03 0.18 - 0.14 0.14 - 0. 07 0.02 0.0 0.58 TOTAL HOURS OF VALID OBSERVATIONS 25482.0 TOTAL HOURS OF ELEVATED RELEASES 22649.6 TOTAL HOURS OF STABILITY ClASS C 259.0 TOTAL HOURS OF ELEVATED STABILITY CLASS C 152.7 METEOROLOGICAL FACILITY: METEOROLOGICAL FACILITY LOCATED 1..3 KH ESE OF BROMNS FERRY NUCLEAR PLANT STABILITY BASED ON DElTA-T BETWEEN 45.30 AHD 89.60 HETERS MIND SPEED AHD DIRECTION HEASURED AT THE 45.67 HETER LEVEL EFFLUEHT VELOCITY = 12.60 H/S

                                                                                                                                   ~
                                                                                                                       ~ ~ I, )~ I
                                                                                                                           )q ~

5 ~ 25'

TABLE 1.3 (Sheet 19 of 22) 30IHT PERCENTAGE FRE UEHCIES Of WIND SPEED BY WIND DIRECTION FOR STABILITY CLASS 0 (-1.5 < DELTA-T< -0.5'C/100 M) BROWHS FERRY NUCLEAR PLANT JAN 1, 77 DEC 31, 79 WIND WIND SPEED (MPH) DIRECTION CAlH 0.6-1.4 1.5-3.4 3.5-5.4 5.5-7.4 7.5-12.4 12.5-18.4 18.5-24.4 >=24.5 TOTAL N O.Q a.a 0.12 0.40 0.62 1.49 0.87 0.12 . 0.0 3.62 HHE 0.0 0.01 0.13 0.46 0.72 1.88 0.91 0.05 0.0 4.16 HE 0.0 0.0 0.09 0.36 0.48 1.04 0.14 0.02 0.0 2.13 EHE 0.0 0.01 0.11 0.24 0.23 0.23 0.04 a.al 0.0 0.87 E 0.0 0.01 0.10 0.20 0.28 0.25 0.05 0.01 Q.a 0.80 ESE 0.0 0.01 0.22 0.52 0.68 1.07 0.16 0.0 0.0 2.66 SE 0.0 0.01 0.67 1.66 0.89 1.75 0.84 Q.16 0.01 5 '9 SSE 0.0 0.01 0.48 0.90 0.63 1.49 1.08 0.26 0.02 4.87 S 0.0 0.0 0.34 0.99 0.67 0.99 0.93 0.33 0.02 4.27 SSW 0.0 0.01 0.20 0.52 0.37 0.69 0.34 0.11 0.0 2.24 SW 0.0 0.01 0.24 0.79 0.43 0.49 0.32 0.05 0.0 2.33 WSW 0.0 0.02 0.16 0.51 0.57 0.57 0.27 0.08 0.0 2.18 W Q.a O.a 0.07 0.36 0.80 1.34 0.55 0.16 0.01 3.29. WHW 0.0 0.0 0.09 0.33 0.48 1.25 0.94 0.32 0.01 3.42 NW 0.0 0.0 0,07 0.36 0.55 1.40 1.44 0.37 0.01 4.20 NNW 0.0 0.0 0.09 0.29 0.53 1.36 1.15 0.19 0.0 3.61 SUBTOTAL 0.0 0.10 3.18 8.89 8.93 17.29 10.03 2.24~ 0.08 50.74 TOTAL HOURS OF VALID OBSERVATIONS 25482.0 TOTAL HOURS OF ELEVATED RELEASES 22649.6 . TOTAL HOURS OF STABILITY CLASS D 13904.1 TOTAL HOURS OF El EVATED STABILITY CLASS 0 12935.5 METEOROLOGICAL FACII ITY: METEOROLOGICAL FACILITY LOCATED 1.3 KM ESE OF BROWNE FERRY NUCLEAR PLANT STABILITY BASED OH DELTA-T BETWEEN 45.30 AHO 89.60 METERS WIND SPEED AHD DIRECTIOH MEASURED AT THE 45.67 METER LEVEL EFFLUEHT VELOCITY = 12.60 M/S

~ ~

I

TABLE 1.3 (Sheet 20 of 22) JOINT PERCENTAGE FRE UEHCIES OF WIND SPEED BY WIND DIRECTION FOR STABILITY CLASS E (-0.5 < DELTA-T< 1.5'C/100 FI) BROWHS FERRY NUCLEAR PLANT PART 2 of 2 ELEVATED RELEASE NODE JAH 1, 77 DEC 31, 79 WIND WIND SPEED (HPN) OIRECTIOM CALM 0.6-1.4 1.5-3.4 3.5-5.4 5.5-7.4 7.5-12.4 12.5-18.4 18.5-24.4 >=24.5 TOTAL H 0.0 0.0 0.13 0.22 0.31 0.80 0.15 0.0 0.0 1.61 HHE 0.0 0.0 0.15 0.24 0.39 1.04 '0. 28 0.0 0.0 2.10 HE 0.0 0.01 0.11 0.25 0.39 0.88 0.18 0,0 0.0 1.82 EHE 0.0 0.0 0.20 0.21 0.33 0.39 0.10 0.0 0.0 1.23 E 0.0 0.0 0.09 0.24 0.30 0.55 0.06 0.0 0.0 1.24 ESE 0.0 0.01 0.29 0.58 0.86 1.10 0.09 0.01 0.0 2.94 SE 0.0 0.02 0. 41 1.04 1.02 1.37 0.55 0.08 0.01 4.50 SSE 0.0 0.01 0.23 0.60 0.54 0.87 0.59 0.14 0.01 2.99 ~ S 0.0 0.01 0.14 0.49 0.32 0.70 0.34 0.05 0.0 2.05 SSW 0.0 0.0 0.11 0.28 0.30 0.48 0.19 ~ 0.01 0.0 1.37 SW 0.0 0.01 0.17 0.27 0.28 0.29 0.09 0.0 0.0 1.11 WSW 0.0 0.01 0.12 0.25 0,24 0.28 0.06 0.0 0.0 0.96'.93 W 0.0 0.0 0.09 0.19 0.26 0.34 0.05 0.0 0.0 WHW 0.0 0.0 0.06 0.13 0.11 0.20 0,04 . 0.01 0.0 0.55 NW 0.0 0.0 0.09 0.14 0.13 0.31 0.08 0.0 0.0 0.75 HNW 0.0 0.0 0.12 0.21 0.16 0.52 0.16 0.0 0.0 1.17 SUBTOTAL 0.0 0.08 2.51 5.34 5.94 10.12 3.01 0.30 0.02 27.32 TOTAL HOURS OF VALID OBSERVATIONS 25482.0 TOTAL HOURS OF ELEVATED RELEASES 22649.6 TOTAL HOURS OF STABILITY CLASS E 7920.9 TOTAL HOURS OF ELEVATED STABILITY CLASS E 6962.9 I METEOROLOGICAL FACILITY: METEOROLOGICAL FACILITY LOCATED 1.3 KH ESE OF BROWNS FERRY NUCLEAR PLANT STABILITY BASED OH DELTA-T BETWEEN 45.30 AHD 89.60 HETERS WIND SPEED AHD DIRECTION HEASURED AT THE 45.67 HETER LEVEL EFFLUEHT VELOCITY = 12.60 H/S I

TABLE l. (Sheet 21 of 22) T T Jff E STABILITY CLASS F ( 1.5 < DELTA-T< 4.0'C/100 H) BROWHS FERRY NUCLEAR PLANT PART 2 of 2 ELEVATED RELEASE NODE 3AH 1, 77 DEC 31, 79 WIND WIND SPEED (HPH) DIRECTION CALH 0.6-1.4 1.5-3.4 3.5-5.4 5.5-7.4 7.5-12.4 12.5-18.4 18.5-24.4 >=24.5 TOTAL N 0.0 0.0 0.03 0.08 0.06 0.34 0.05 0.0 0.0 0.56 HNE 0.0 0.0 0.04 0.06 0.11 0.42 0.21 0.0 0.0 0.54 NE 0' 0.0 0.0 0.0 0.04 0.04 0.10 0.11 0.15 0.40 0.12 0.0 0.0 0 '1 EHE 0.11 0.29 0.07 0.0 0.0 0.62 E 0.0 0.0 0.03 0.07 0.11 0.32 0.02 0.0 0.0 0.55 ESE 0.0 0.0 0.13 0.26 0.24 0.24 0.0 0.0 0.0 0.87 SE 0.0 0.0 0.13 0.38 0.30 0.19 0.0 0.0 0.0 1.00 SSE 0.0 ~ 0.0 0.09 0.11 0.12 0.14 0.03 0.0 0.0 0.49 S 0.0 0.0 0.08 0.11 0.13 0.21 0.03 0.0 0.0 0.56 SSW 0.0 0.0 0.04 0.12 0.14 0.24 0.01 ',0.0 0.0 0.55 0.0 0.0 0.04 0.09 0.10 0.06 0.0 SW WSW 0.0 0.0 0.0 0.01 0.03 0.04

                                       '.07           0.06          0.05          0.0 0.0 0.0 0.0 0.0 0.29 0.21 W                                          0.04        0.05          0.04          0.0          0.0    0.0               '.18 WHW          0.0       0.0      0.02       0.04        0.01          0.01          0.0          0.0    0.0        0.08 NW           0.0       0.0      0.03       0.04        0.03          0.02          0.0          0.0    0.0        0.12 HHW          0.0       0.0      0.02       0.02        0.04          0.10          0.0          0.0    0.0        0.18 SUBTOTAL     0.0       0.01     0.83       1.70        1.76          3.07          0.54         0.0    0.0        7.91 TOTAL  HOURS OF VALID OBSERVATIONS                                    25482.0   ~

TOTAL HOURS OF ELEVATED RELEASES 22649.6 TOTAL HOURS OF STABILITY CLASS F 2385.0 TOTAL HOURS OF ELEVATED STABILITY CLASS F 2028.0 I METEOROLOGICAL FACILITY: METEOROLOGICAL fACILITY LOCATED 1.3 KH ESE Of BROWHS FERRY NUCLEAR PLANT STABILITY BASED OH DELTA-T BETWEEN 45.30 AHD 89.60 HETERS WIND SPEED AHD DIRECTION HEASURED AT THE.45.67 HETER LEVEL EFFLUEHT VELOCITY = 12.60 M/S 4

                                                )                                                        II (
                                                                                                              ~
                                                                                                                      ~      f

TABLE l. (Sheet 22 of 22) JOINT PERCENTAGE FRE UEHCIES OF WIND SPEED BY WIND DIRECTION FOR STABILITY CLASS G (DELTA-T> 4.0'C/100 M) BROWHS FERRY NUCLEAR PLANT PART 2 of 2 ELEVATED RELEASE MODE JAH 1, 77 DEC 31, 79 WIND WIND SPEED (MPH) OIRECTIOM CALM 0.6-1.4 1.5-3.4 3.5-5.4 5.5-7.4 7.5-12.4 12.5-18.4 18.5-24.4 >.=24.5 TOTAL N 0.0 0.0 0.0 0.0 0.02 0.06 0.01 0.0 0.0 0.09 HHE 0.0 0.0 0.01 0.02 0.04 0.11 0.04 0.0 0.0 0.22 NE 0.0 0.0 0.02 0.02 0.03 0.12 0.02 0.0 0.0 0.21 ENE 0.0 0.0 0.0 0.02 0.02 0.07 0.02 0.0 0 0

                                                                                                     ~     0 13
                                                                                                             ~

E 0.0 0.0 0.0 0.02 0.01 0.04 0.0 0.0 0.0 0.07 ESE 0.0 0.01 0.05 0.15 0.07 0.01 0.0 0.0 0.0 0.29 SE 0' 0.0 0.12 0.20 0.13 0.04 0.0 0.0 0.0 0.49 SSE 0.0 0.0 0.03 0.06 0.06 0.02 0.0 0.0 0~0 0.17 S 0.0 0.0 0.02 0.07 0.06 0.01 0.0 0:0 0.0 0.16 SSW 0.0 0.0 0.0 0.02 0.02 0.06 0.0 ',0.0 0.0 0.10 SW 0.0 0.0 0.01 0.01 0.03 0.02 0.0 0.0 0.0 0.07 WSW 0.0 0.0 0.01 0.0 0.0 0.0 0.0 0.0 0.0 0.01. W 0.0 0.0 0.01 0.0 0.01 0.0 0.0 0.0 0.0 0.02 WNW 0.0 0.0 0.02 0.0 0.0 0.0 0.0 0.0 0.0 0.02 HW 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 HHW 0.0 0.0 0.01 0.01 0.0 0.01 0.0 0.0 0.0 0.03 SUBTOTAL 0.0 0.01 '.31 0.60 0.50 0.57 0.09 0.0 0.0 2.0B TOTAL HOURS OF VALID OBSERVATIONS 25482.0 . TOTAL HOURS OF ELEVATED RELEASES 22649.6 TOTAL HOURS OF STABILITY CLASS G 694.7 TOTAL HOURS OF ELEVATED STABILITY CLASS G 543.1 I METEOROLOGICAL FACILITY: METEOROLOGICAL FACILITY LOCATED 1.3 KM ESE OF BROWNS 'FERRY NUCLEAR PLANT STABILITY BASED OH DELTA-T BETWEEN 45.30 AHD 89.60 METERS WIND SPEED AHD DIRECTION MEASURED AT THE 45.67 METER I EVEL EFFLUEHT VELOCITY = 12.60 M/S 2 7, I

TABLE 1.4 BFH OFFSITE RECEPTOR LOCATION DATA GROUND LEVEL ELEVATED POINT SECTOR DIST. m ELEY. m s/m'/q x/0 1/m~ x/O s/m~ 1 Site Boundary H 1525. 7. 1.60E-06 5.64E-09 9.79E-ll 8.57E-10 2 Site Boundary NHE 1300. 7.88E-07 1.97E-09 7.86E-12 5.24E-10 3 Site Boundary NE 1250. 7. 4.52E-07 1.56E-09 5.91E-12 4.66E-10 Site Boundary ENE 1450. 0. 7.30E-07 2.92E-09 . 1.37E-ll 4.11E-10 5 Site Boundary E 1375. 0. 8.24E-07 4.04E-09 8.84E-12 4.75E-10 6 Site Boundary ESF 1575. 0. 4.56E-07 3.28E-09 4.98E-ll 5.98E-10 7 Site Boundary SE 5600. -6. 7.61E-08 3.63E-10 7.24E-09 ~ 3.00E-10 8 Site Boundary SSE 2875. -6. 4.86E-07 1..77E-09 1.58E-09 5.59E-10, 9 Site Boundary S 2850. -6. 8.27E-07 2.246-09 1.12E-09 6.67E-10 10 Site Boundary SSM 2425. -6. "1.08E-06 2.92E-09 9.27E-10 7.07E-10 ll Site Boundary SM 2300. -6. 6.87E-07 1.75E-09 5.94E-10 6.06E-10 12 Site Boundary MSM 2500. -6. 6.38E-07 1.14E-09 5.34E-1.0 3.45E-10 13 Site Boundary W 2550. -6 6.70E-07 1.25E-09 5.06E-10 2.74E-10-- 14 Site Boundary MNM 3325. -6. 3.69E-07 '9.07E-10 2.69E-09 4.75E-10 15 Site Boundary HM 2275. -6. 1.69E-06 4.92E-09 1.10E-09 1.24E-09 16 Site Boundary NNW 1650. 0. 1.84E-06 5.29E-09 1.31E-10 1.05E-09 17 Air Dose Point NW 5100. 16. 5.42E-07 1.22E-09 .2.01E-08 6.30E-10 18 Air Dose Point HM 5500 16. 4.89E-07 1.06E-09'.82E-10 2.05E-08 5.59E-10 19 Air Dose Point HM 6100 16. 4.25E-07 2.08E-08 4.75E-10 20 Air Dose Point NW 6500. 16. 3.89E-07 7.87E-10 2.08E-08 4.29E-10 21 Air Dose Point NM 6800. 16. 3.66E-07 7.25E-10 2.07E-08 4.00E-10 22 Air Dose Point NM 7100. 16. 3.45E-07 6.71E-10 2.05E-08 3.-73E'-10 23 Resident, Garden H 1620. 13. 1.46E-06 5.11E-09 2.89E-10 8'.98E-10 24 Resident HHE 2845. 13. 2.46E-07 5.34E-10 3.91E-09 6.14E-10 25 Resident HE 4075. 13. 7.68E-OB 2.13E-10 7.85E-09 3.92E-10 26 Resident, Garden EHE 1960. 13. 4.61E-07 1.78E-09 5.62E-10 4.79E-10 27 Resident, Garden E 4437. 19. 1.43E-07 5.54E-10 9.50E-09 3.37E-10 28 Resident ESE 4655. -1 2. 8.82E-OB 5.17E-10 5.01E-09 3.62E-10 29 Resident SE 8100. 0. 4.55E-OB 1.87E-10 8.54E-09 1.67E-10 30 Resident, Garden SSE 7155. 0. 1.39E-07 3.54E-10 7.23E-09 1.75E-10'.10E-10 31 Resident, Garden S 4460. 0. 3.91'E-07 8.54E-10 6.74E-09 32 Resident, Garden SSW 4155. 0. 5.24E-07 1.15E-09 6.32E-09 4.66E-10 33 Resident SM 4896. 7. 2.43E-07 4.74E-10 7.92E-09 3.28E-10 34 Resident;Garden WSM 4131. 0. 3.24E-07 4.77E-10 3.27E-09 2.31E-10 35 Resident W 2550. -24. 6.70E-07 1.25E-09 1.91E-10 2.74E-10 36 Resident, Garden WNW 4425. 10. 2.48E-07 5.52E 10 7.61E-09 3.45E-10 37 Resident, Garden NW 3500. -9. 9.17 E-07 2.35E-09 5.87E-09 9.76E-10 38 Resident, Garden NNW 1650. -9. 1.84E-06 5.29E-09 5.91E-11 1.05E-09 39 Garden HE 4475. 13. 6.70E-08 1.81E-10 8.80E-09 3.53F-10 40 Garden NNE 2980. 0 2.30E-07 4.93E-10 2.68E-09 6.07E-10 41 Garden SW 5430. 0. 2.12E-07 3.93E-10 7.28E-09 2.79E-10 42 Garden W 2675 0. 6.27E-07 1.15E-09 8.56E-10 2.72E-10 43 Hi lk Cow Child H 8045. 0. 1.47E-07 3.16E-10 1.25E-08 2.30E-10 44 Milk Cow Infant EHE 9450 21. 4.71E-08 1.14E-10 8.42E-09 8.94E-11 45 Hilk Cow Child HNW 10975 30. 1.32E-07 1.97E-10 1.69E-OB 1.65E-10 10975 0. 1.86E-08 3.70E-ll 7.77E-09 9.04E-ll

TABLE 1.5 DOSE FACTORS FOR SUBMERSION IN NOBLE GASES DFBa DFb DFSa '. DFb Kr-85m 1 17E+03c 1.21E+03 1.46E+03 3.86E+03 Kr-85 1.61E+01 1.69E+01 1.34E+03 3.83E+03 Kr-87 5.92E+03 6.05E+03 9.73E+03 2.01E+04 Kr-88 1.47E+04 1.50E+04 2.37E+03 5.72E+03 Kr-88+D 2.02E+04 3.72E+04 Kr-89 1.66E+04 1.59E+04 1.01.E+04 1.88E+04 Xe-131m 9.15E+01 1.53E+02 4.76E+02 2.18E+03 Xe-133m 2.51E+02 3.17E+02 9.94E+02 2.90E+03 Xe-133 2.94E+02 3.46E+02 3.06E+02 2.06E+03 Xe-135m 3.12E+03 3.30E+03 7.11E+02 1.45E+03 t Xe-135 Xe-137 Xe-138 Xe-138+D Ar-41 1.81E+03 1.42E+03 8.83E+03 8.84E+03 1.88E+03

                                           '.48E+03 9.DOE+03 2.65E+04 9.76E+03 1.86E+03 1.22E+04 4.13E+03 2.69E+03 4.84E+03 2.50E+04 9.25E+03 2.81E+04 5.54E+03
                                                                                    .'" =-

mrem/yr per per yCi/m' yCi/m'rad/yr 1 17E+03 = 1.17 X 10'.

TABLE 1.6 HUCLIDE SPECIFIC TRANSFER DATA~ (Sheet 1 of 2) NUCLIDE RETEHTIOH Biv so11 'i L 1 Tritium 4.70E-01 '4. 80E+00 1.30E-02 2 C-14 4.70E-01 5.50E+00 1.20E-02 3 H-1 3 4.70E-01 7.50E+00 2.20E-02 4 0-1 9 4.70E-01 1.60E+00 2.00E-02 5 F-18 4.70E-01 6.50E-04 1.40E-02 6 Ha-24 4.70E-01 5.20E-02 4.00E-02 7 P-32 4.70E-01 1.10E+00 2.50E-02 8 Ar-41 4.70E-01 6.00E-01 2.00E-02 9 Cr-51 4.70E-01 2.50E-04 2.20E-03 10 Ha-54 4.70E-01 2.90E-02 2.50E-04

,11   Hn-56    4.70E-01        2:90E-02    .2,.50E-04 12  Fe-59    4.70E-01        6.60E-04     1.20E-03 13  Co-58    4.70E-01        9.40E-03     1.00E-03 14  Co-60    4.70E-01        9.40E-03     1.00E-03 15  Zn-69m   4.70E-01        4.00E-01   '.90E-02 16  Zn-69    4.70E-01        4.00E-01     3.90E-02 17  Br-84    4.70E-01        7.60E-01     5.00E-02 18  Br-85    4.70E-01        7.60E-01     5.00E-02 19  Kr-85m   4.70E-01        3.DOE+00     2.00E-02 20  Kr-85    4.70E-01        3.00E-OO     2.00E-02 Kr-87    4.70E-01        3.00E-OO     2.00E-02 Kr-88    4.70E-01        3.00E-OO     2.00E-02 Kr-89    4.70E-01        3.00E-OO     2.00E-02 Rb-88    4.70E-01        1.30E-01     3.00E-02 25  Rb-89    4.70E-01        1.30E-01     3.00E-02 26  Sr-89    4.70E-01        1.70E-02     1.40E-03 27  Sr-90    4.70E-01        1.70E-02     1.40E-03 28  Sr-91    4.70E-01        1.70E-02     1.40E-03 29  Sr-92    4.70E-01        1.70E-02     1.40E-03 30  Sr-93    4.70E-01        1.70E-02     1.40E-03 31   Y-90    4.70E-01        2.60E-03     1.00E-05 32   Y-91m   4.70E-01        2.60E-03     1.00E-05 33   Y-91    4.70E-01        2.60E-03     1.00E-05 34   Y-92    4.70E-01        2.60E-03     1.00E-05 35   0-93    4.70E-01        2.60E-03     1.00E-05 36  Zr-95    4.70E-01        1.70E-04     5.00E-06 37  Hb-95m   4.70E-01        9.40E-03     2.50E.-03 38  Hb-95    4.70E-01        9.40E-03     2.50E-03 39  Ho-99    4.70E-01        1.20E-01     7.50E-03 40  Tc-99m   4.70E-01        2.50E-01     2.50E-02 41  Tc-99    4.70E-01        2.50E-01     2.50E-02 42  Tc-104   4.70E-01        2.50E-01     2.50E-02 43  Ru-106   4.70E-01        5.00E-02     1.00E-06 44  Te-132   4.70E-01        1.30E+00     1.00E-03 45   I-1 29  4.70E-01        2.00E-02     1.20E-02

~" 46 I-1 31 HI-1 31 4.70E-01 4.70E-01 2.00E-02 2.00E-02 1.20E-02 1.20E-02

TABLE 1.6 NUCLIDE SPECIFIC TRANSFER DATA* (Sheet 2 of 2) HUCLIDE RETEHTIOH Bi v s i 1 FM 48 I-1 32 4.70E-01 '2.00E-02 1.20E-02 49 MI-1 32 4.70E-01 2.00E-02 1.20E-02 50 I-133 4.70E-01 2.00E-02 1.20E-02 51 MI-133 4.70E-01 2.00E-02 1.20E-02 52 I-134 4.70E-Ol 2.00E-02 1.20E-02 53 MI-134 4.70E-01 2.00E-02 1.20E-02 54 I-135 4.70E-01 2.00E-02 1.20E-02 55 MI-135 4.70E-01 2.00E-02 1.20E-02 56 Xe-131m 4.70E-01 1.00E+01 2.00E-02 57 Xe-133m 4.70E-01 1.00E+01 2.0QE-02 58 Xe-133 4.70E-01 1". 00E+01 2.00E-02 59 Xe-135m 4.70E-01 1.00E+01 2.00E-02 60 Xe-135 4.70E-01 1.00E+01 2.00E-02 61 Xe-137 4.70E-01 1.00E+01 2.00E-02 62 Xe-138 4.70E-01 1.00E+01 2.00E-02 63 Cs-134 4.70E-01 1.00E-02 8.00E-03 64 Cs-135 4.70E-01 1.00E-02 8.00E-03 65 Cs-136 4.70E-01 1.00E-02 8.00E-03 66 Cs-137 4.70E-01 1.00E-02 8.00E-03 67 Cs-138 4.70E-01 1.00E-02 8.00E-03 Ba-139 4.70E-01 5.00E-03 4.00E-04 Ba-140 4.70E-01 5.00E-03 4.00E-04 La-140 4.70E-01 2.50E-03 5.00E-06 71 Ce-144 4.70E-01 2.50E-03 1.00E-04 72 Pr-143 4.70E-01 2.50E-03 5.00E-06 73 Pr-144 4.70E-01 2.50E-03 5.00E-06 74 Hp-239 4.70E-01 2.50E-03 5.00E-06

Reference:

HUREG/CR-1004

Reference:

Regulatory Guide 1.109

~"

Reference:

HUREG/CR-1004 for Iodine, Strontium, and Cesium; R.G. 1.109 for all other nuclides.

TABLE 1.7 EXTERNAL DOSE FACTORS FOR STANDING ON CONTAMINATED GROUND (mrem/h per pCi/m~) (Sheet 1 of 2) Element Total Bod DFGi Skin H-3 0.0 0.0 C-14 0.0 0.0 Na-24 2.50E-08 2.90E-08 P-32 0.0 0.0 Cr-51 2.20E-10 2. 60E-1 0

.Hn-54                 5.80E-09                               6.80E-09 Hn-56                 1.10E-08                               1.30E-OB Fe-55                 0.0                                    0.0 Fe-59                 8.00E-09                               9.40E-09 Co-58                 7.00E-09                               8.20E-09 Co-60                 1.70E-08                               2.00E-OB 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-ll                               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 Rb-88                  3.50E-09                               4.00E-09 Rb-89                  1.50E-OB                               1.80E-08 Sr-89                  5.60E-13                               6.50E-13 Sr-91                  7.10E-09                               8.30E-09.

SI -92 9.00E-09 1.00E-OB Y-90 2.20E-12 2.60E-12 Y-91H 3.80E-09 4.40E-09 Y-91 2.40E-ll 2.70E-11 Y-92 1.60E-09 1.90E-09 Y-93 5.70E-lo 7.80E-10 Zr-95 5.00E-09 5.80E-09 .Zr-97 5.50E-09 6.40E-09 Nb-95 5.10E-09 6.00E-09 Ho-99 1.90E-09 2.20E-09 Tc-99H 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-llOH 1.80E-08 2.10E-OB Te-125M 3.50E-11 4.80E-ll Te-127H 1.10E-12 1.30E-12 Te-127 1.00E-11 1.10E-11 Te-129H 7.70E-10 9.00E-10 Te-129 7.10E-10 8.40E-10 Te-131M 8.40E-09 9-90E-09 Te-131 2.20E-09 2.60E-06

TABLE 1.7 BATERHAL DOSE FACTORS FOR STANDIHG OH COHTAHIHATED GROUND (mrem/h per pCi/m') (Sheet 2 of 2) Element Total Bod DFGi Skin T e-132 1.70E-09 2.00E-09 I-130 1.40E-08 1.70E-OB I-131 2.80E-09 3.40E-09 I-1 32 1.70E-OB 2.00E-OB I-1 33 3.70E-09 4.50E-09 I-1 34 1.60E-OB 1.90E-OB I-1 35 1.20E-08 1.40E-OB Cs-134 1.20E-08 1.40E,-OB Cs-136 1.50E-08 1.70E-08 Cs-137 4.20E-09 4.90E-09 Cs-138 2.10E-08 2.40E=OB Ba-139 2.40E-09 2.70E-09 Ba-140 2.10E-09 2.40E-09 Ba-141 4.30E-09 4.90E-09 Ba-142 7.90E-09 9.00E-09 La-140 1.50E-OB 1.70E-OB La-142 1.50E-OB 1.80E-08 Ce-141 5.5QE-10 6. 20E-1 0 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 Hd-1 47 1.00E-09 1.20E-09 M-1 87 3.10E-09 3.60E-09 - Hp-239 9.50E-10 1.10E-09

TABLE 2.1 DOSE COHHITHENT FACTORS (REH(HICROCI) HALF-LIFE (Sheet I of .4) NUCLIDE (DAYS) ADULT CHILD BONE Gl TRACT TIIYROID TOTAL BODY LI VER BONE Gl TRACT TIIYROID TOTAL BODY LIVER II-3 4.50ft03 1.05E-04 1.05E-04 1.05E-04 1.05E-04 1.05E-04 2.03E-04 2.03E-04 2.03E-04 2.03E-04 2.03E-04 C-I4 2.08ft06 2.84E-03 5.68E-O4,a 5.68E-04 5.68E-O4 5.68E-04 1.2IE-O2 2.42E-03 $ .42E-03 2.42E-03 2.42E-03 Ne-22 9.49ft02 2.50E-02 1.35E-02 1.2IE-02 1.36E-02 1.40E-02 2.50E-02 1.35E-02 1.2IE-02 1.36E-02 1.40E-02 Ne-24 6.26E-OI 1.70E-03 t.70E-03 1.70E-03 1.70E-03 1.70E-03 5.80E-03 5.80E-03 5.80E-03 5.80E-03 5.80E-03 P-32 1.43ftOI 1.93E-OI 2.17E-02 7.46E-03 7.46E-03 1.20E-02 8.25E-OI 2.28E-02 3.18E-02 3. 18E-02 3,86E-02 Cr-51 2.77fiot 2.66E-06 6.68E-04 1.59E-I6 2.66E-06 2.66E-06 8.90E-06 4,72E-04 4.94E-06 8. 90E-06 8.90E-06 Hn-54 3.12E<02 8.72E-04 1,40f-02 8.72E-O4 8.72E-04 4.57E-03 2.85E-03 8.98E-03 2.85E-03 2.85E-03 1.07E-02 Hn-56 1.OBEAH I 2.04E-05 3.67E-03 2.04E-05 2.04E-05 I. 15E-04 7.54E-05 4.84E-02 7.54E-05 7.54E-05 3.34E-04 Fe-55 9.86402 2.75E-O3 1.09E-O3 4.43E-04 4.43E-04 1.90E-03 1.15E-O2 1.13E-03 1.89E-03 1.89E-03 6.IOE-03 Fe-59 4.46ftOI 4.34E-03 3.40E-02 3.9IE-03 3.91E-03 1.02E-02 1.65E-02 2.78E-02 1.33E-02 1.33E-02 2.67E-02 Co-57 2.7 If&2 3.57E-04 4.56E-03 I.IOE-04 1.84E-04 2.53E-04 3.57E-04'.5 4.56E-03 I.IOE-04 1.84E-04 2.53E-04 Co-58 7.08EA I 1.67E-O3 1.5IE-02 1.67E-03 1.67E-03 7.45E-04 IE-03 1.05E-02 5.5 IE-03 5.5IE-03 1.80E-03 Co-60 1.92EA3 4.72E-03 4.02E-02 4.72E-03 4.72E-03 2.14E-03 1.56E-02 2.93E-02 1.56E-02 1.56E-02 5.29E-03 Nl-63 3.65ft04 1.30E-OI 1.88E-03 4.36E-03 4.36E-03 9.0IE-03 5.38E-OI 1.94E-03 1.83E-02 1.83E-02 2.88E-02 Nl-65 1.05E-OI 5.28E-04 1.74E-03 3. 13E-05 3. 13E-05 6.86E-05 2.22E-03 2.56E-02 1.22E-04 1.22E-04 2,09E-04 Cu-64 5.30E-OI 3.9IE-05 7.IOE-03 3.9IE-05 3.9IE-05 8.33E-05 1.48E-04 1.15E-02 1.48E-04 1.48E-04 2.45E-04 Zn-65 2.44ft02 4.84E-03 9.70E-03 6.86E-03 6.96E-03 1.54E-02 1.37E-02 6.4 If-03 2.27E-03 2.27E-03 3.65E-02 Zn-69 3.96E-02 1.03E-05 2.96E-06 1.37E-06 1.37E-06 1.97f-05 4,38E-05 3.99E' 5.85E-06 5.85E-06 6.33E-05 As-74 1.78E<0t 2.90E-O4 3.88E-02 2.90E-04 2.90E-04 2.5IE-04 2.90E-04 3.88E-02 2.90E-04 2.90E-04 2.51E-04 As-76 I. IOE F00 4.49E-05 9.70E-02 4.49E-05 4.49E-05 4.70E-05 4.49E-05 9.70E-O2 4.49E-05 4.49E-05 4.70E-05 Br-83 I.OOE-OI 4.02E-05 5.79E-05 4.02E-05 4.02E-05 4.02E-05 1.7IE-04 0.00ft00 t.71E-04 1,7IE-04 1.7 IE-04 Br-84 2.2IE-02 5.2IE-05 4.09E-IO 5.2IE-05 5.2IE-05 5.2IE-05 1.98E-04 0.00ft00 1.98E-04 1.98E-04 1.98E-04 Br-85 1.99E-03 2.14E-O6 I.OOE-21 2. 14E-06 2. 14E-06 2. 14E-06 9.12E-06 0.00fiOO 9,12E-06 9.t2E-06 9.12E-06 Kr-839 7.75E-O2 0.00ftOO 1.46E-04 O.DOE~ O.DOE tOO O.OOEt00 0.00ftOO 1.46E-04 0.00ft00 0.00ft00 0.00ftOO Kr-85m 1.87E-OI O.DOE+00 3.30E-03 O.OOE>00 0.00E<00 0,00ft00 O,OOEt00 3.30E-03 0.00ft00 0.00ft00 O.OOE<00 Kr-85 3.9tft03 0.00ft00 4.62E-02 O.OOE <00 O,OOE<00 0.00fi00 O.OOE<00 4.62E-02 0.00ft00 0.00E>00 O.OOE<00 Rb-86 1.87ftOI 9.83E-03 4.16E-03 9.83E-03 9.83E-03 2.IIE-02 4. 12E-02 4.3IE-03 4.12E-02 4.12E-02 6.70E-02 Rb-88 1.23E-O2 3.2IE-05 8.36E-16 3.2IE-05 3,2IE-05 6,05E-05 1.32E-04 9.32E-06 1.32E-04 1.32E-04 1.90E-04 Rb-89 1.07E-02 2.82E-05 2.33E-IB 2.82E-05 2.82E-05 4.0IE-05 1,04E-04 1.02E-06 1.04E-04 1.04E-04 1.17E-04 Sr-89 5.05EA I 3.08E-OI 4.94E-02 8.84E-03 8.84E-03 8.84E-03 1,32fi00 5.IIE-02 3.77E-02 3,77E-O2 3.77E-02 Sr-90 1.06E+04 7.58E+00 2.19E-OI I.86ft00 1.86ft00 1.86ft00 1.70E<OI 2.29E-OI 4.3IE<00 4.3IE<00 4. 3lft00 Sr-9t 3.97E-Ot 5.67E-03 2.70E-02 2.29E-04 2.29E-04 2.29E-04 2.40E-02 5.30E-02 9.06E-04 9.06E-04 9.06E-04 Sr-92 I. 13E-Ol 2. 15E-03 4.26E-02 9.30E-05 9.30E-O5 4.30E-05 9.03E-03 1.7IE-OI 3.62f-04 3.62E-04 '3.62E-04 Y-90 2.67E~ 9.62E-06 1.02E-OI 2.58E-07 2.58E-07 2. 58EW7 4. I IE-05 I. 17E-Ol I.IOE-06 I,IOE-06 I. IOE-06 Y-91 5.86EAI 1.4 I E-04 7.76E-02 3.77E-06 3.77E-06 3.77E-06 6.02E-04 8.02E-02 1.61E&5 1.6IE-05 1.6IE-05 I

't~

TABLE 2.1 DOSE CQHHITHENT FACTORS (REHIHICRQCI) IIALF-LIFE (Sheet 2 of 4) NUCLIDE (DAYS) ADULT CIIIL0 SON f Gl TRACT TIIYROID TOTAL BODY LIVER BONE Gl TRACT TIIYROID TOTAL BODY LIVER Y-9IH 3.45E-02 9.09E-OB 2.67E-07 3.52E-09 3.52E-09 3.52E-09 3.02E-07 7.48E-04 1.39E-OS 1.39E-QB 1.39E-OB Y-92 1.40E-OI 1.48E-02 2.47E-QB 2,47E-QB 2.47E-QB 2.47E-QB 3.60E-06 1.04E-OI i) .03E-07 1,03E-07 I. 03E-07 Y-93 4.2IE-OI 2.6SE-06 8. 7.40E-OB 7.40E-QB 7.40E-QB 1.14E-05 1.70E-OI 3.13E-07 3.13E-07 3. 13E-07 50E-02'.09E-02 Zr-95 6.40EA I 3.04E-05 6.60f-06 6.60f-06 9.75E-06 1.16E-04 2.66E-02 2.27E-05 2.27E-05 2,55E-05 Zr-97 7.00E-OI 1.68E-06 1.05E-OI 1.55E-07 1.55f-07 3.39E-07 6.99E-06 1.53E-OI 5.96E-07 5.96E-Q7 I .0 IE-06 Nb-95 3.50E<00 (j.22E-06 2. IOE-02 1.86E-06 1.86E-06 3.46E-06 2.25E-05 1.62E-02 6.26E-06 6.26E-06 8.76E-06 Nb-95m 3.61E<00 5.95E-07 2.43E-OZ 2.54E-07 2.54E-07 4.6'k-02 5.95E-07 2.43E-OZ 2.54E-07 2.54'E-07 4.63E-07 Nb-97 5.IIE-02 1.56E-05 1.43E-03 7.85E-07 2.90E-05 1.62E-05 1.56E-05 1.43E-03 7.85f-07 2.90E-05 1.62E-05 Nb-97m 6.25E-04 3.48E-07 2.71E-05 3. 12E-08 6.28E-07 4.73E-07 3.40E-07 2.7IE-05 3.12E-QS 6,20E-07 4.73E-07 Ho-99 2.75fo00 8.20E-04 9.99E-03 8.20E-04 8.20E-04 4.3IE-03 3.29E-03 I. IQE-02 3.29E-03 3.29E-03 1.33E-02 Tc-99 7.77E(07 4. IQE-04 3.20E-03 1.4 IE-02 2. 14f-04 6.28E-04 4.10E-04 3.20E-03 1.4IE-02 2. 14E-04 6,20E-04 Tc-99m 2.5 I E-01 2.47E-07 4. 13E-04 8.89E-06 8.89E-06 6.98E-02 9.23E-07 1.03E-03 3.00E-05 3.00E-05 I.BIE-06 Ru-103- 3.94fiOI 1.85E-04 2.16E-02 7.97E-05 7.97E-05 7.97E-05 7.3IE-'04 1.89E-02 2.81E-04 2.81E-04 2,8IE-04 Ru-105 1.85E-OI 1.54E-05 9.42E-03 6.08E-06 6.00E-06 6.00E-06 6.45E-05 4.2IE-02 2.34E-05 2. 34E-05 2.34E-05 Ru-106 3.68ft02 2.75E-03 1.78E-OI 3.48E-04 3.40E-04 3.48E-04 I. 17E&2 1.82E-OI 1.46E-03 1.46E-03 1.46E-03 Rhl03m 3.89E-02 4.05E-QB 9.27E-05 1.58E-OB 8.96E-07 2,2IE-OB 4.05E-OB 9.27E-05 .1.50E-QS 8.96E-07 2.2IE-QS Rh-105 1.40E<00 5.68E-05 1.4 IE-02 1.30E-05 I.QZE-04 3.35E-05 5.6BE-05 . 1.4IE-02 1.30E-05 1.02E-04 3.35E-05 Rhl05m 4.40E-04 2.72E-OB 7.7SE-06 4.91E-09 6.34f-08 2.00E-QB 2.72E-QB 7.78E-06 4.9IE-09 6.34E-OB 2.00E-OS Rh-106 3.46E-04 1.86E-QB 7.20E-05 2.80E-09 1.89E-07 3.57E-QB 1.86E-QB 7.20E-05 2.80E-09 1.89E-07 3.57E-QB AgllQm 2.52ft02 1.60E-04 6.04E-02 8.79E-05 8.79f-05 1.40E-04 5.39E-04 4.33E-02 2.9IE-04 2.9IE-04 3.64E-04 Ag-III 7.47E<00 5.65E-05 4.85E-02 1.26E-05 1.26E-05 2.46E-05 5.65E-05 4.85E-02 1.26E-05 1.26E-05 2.46E-05 Sb-122 2.72ft00 2.29E-04 6.4IE-02 3. IIE-06 6.70E-05 4.51E-06 2.29E-04 6.47E-OZ 3. IIE-06 6.70E-05 4.5IE-Q6 Sb-124 6.02EA I 2.75E-03 9.70E-02 7.14E-06 1.16E-03 5.47E-07 2.75f-03 9.70E-02 7.14E-06 1.16E-03 5.47E-07 Sb-127 3.80E+00 5.45E-04 7.00E-02 1.19E-04 6.13E-04 2.95E-04 5.45E-04 7.00E-02 1.19E-04 6.13E-04 2.95E-04 Te125m 5.80ftOI 2.69E-03 1.07E-02 8.06E-04 3.59E-04 8,7 IE-04 1.14E-02 I.IQE-02 3.20E-03 1.52E-03 3.Q9E-03 Te-127 3.92E-OI I.IQE-04 8.6SE-03 8.. 15E-05 2.30f-05 3.95E-05 4.7IE-04 1.04E-02 3.26E-04 I.OIE-04 1.27E-04 Te 127m 1.09402 6.77E-03 2.27E-02 1.73E-03 8.25E-04 2.42E-03 2.89E-02 2.34E-02 6.91E-03 3.43E-03 7. 28E-03 Te-129 4.86f-02 3. 14E-05 2.37E-05 2.4IE-05 7.65E-06 I.ISE-05 1.34E-03 8.34E-03 9.56E-05 3.ISE-05 3,74E-05 Tel29m 3.34EAI 1.15E-02 5.79E-02 3.95E-03 1.82E-03 4.29E-03 4.87E-02 5.94E-02 1.57E-02 7.56E-03 1.36E-02 To-131m 1.25ft00 1.73E-03 8.40E-OZ 1.34E-03 7.05f-04 8.46E-04 7.20E-03 I.OIE-OI 5. 12E-Q3 2.65E-03 2.49E-03 Te-131 1.74E-02 1.97E-05 2.79E-06 1.62E-05 6.22E-06 8.23E-06 8.30E-05 4.36E-04 6.35E-05 2.47E-05 2,53E-05 Te-132 3.25E QO 2.52E-03 2.7IE-02 I.BQE-03 1.53E-03 1.63E-03 I. DIE-02 4.50E-02 6.51E-03 5.40E-03 4.47E-03 1-129 5.80E+09 9.42E-04 7.84E-05 7.80E+00 3.ISE-03 7.24E-,04 9.42E-04 7.84E-05 7.80E~ 3. I BE-03 7.24E-04 1-130 5.15E-OI 7.56E-04 1.92E-03 1.89E-OI B.BQE-04 2.23E-03 2.92E-03 2.76E-03 6.50E-OI 3.04E-04 5.90E-03 1-131 S.O4E+00 4. 16E-03 1.57E-03 1.95EAO 3.4IE-03 5.95E-03, 1.72E-OZ 1.54E-03 5.72E<00 9.83E-03 1.73E-Q2

                                                                                                         ~ v I

DOSE COHHllHENT FACTORS (REHIHICROCI) HALF-LIFE (Sheet 3 of 4) NUCLIDE (DAYS) ADULT CIIILD BONE Gl 'IRACT TIIYROI9 T OTAL BODY LIVER BONE GI TRACT TIIYROID TOTAL BODY LIVER 1-132 9.54E-02 2.03f-04 1.02E-04 1.90E-OZ 1.90E-04 5.43E-04 8.00E-04 1.73E-03 6.82E-02 6.76E-04 1.47E-03 1-133 8.67E-OI 1.42E-03 2.22E-03 p 3.63E-OI 7.53E-04 2.47E-03 5.92E-03 2.95E-03 i,.36E 00 2,77E-03 7.32E-03 1-134 3.65E-OZ 1.06E-04 2.5IE-07 4.99E-03 1.03E-04 2.88E-04 4.19E-04 5.16E-04 1.79E-02 3,58E-04 7.78E-04 1-135 2.74E-OI 4.43E-04 1.3IE-03 7.65E-02 4.28E-04 1. 16E-03 1.75E-03 2.40E-03 2.79E-OI 1.49E-03 3.15E-03 Xel33m 2.19E<00 O.DOE<00 2.45E-02 0.DOE<00 O.DOE<00 O.DOE<00 O.DOE<00 2.45E-02 O.DOE<00 O.DOE<00 0.00E<00 Xe-133 5.25E<00 g.DOE<00 2.58E-02 O.DOE<00 O.DOE<00 0.00f <00 0.00f<00 2.58E-02 O.DOE<00 0.DOE<00 O.DOE<00 Xe135m 1.06E-02 O.DOE<DO 3.29E-04 0.00E<00 O.DOE<00 O.DOE<00 O.OOE<00 3.29E-04 O.DOE<00 0.00f<00 O.DOE<00 Xe-135 3.79E-OI 0.00E<00 I.OOE-02 O.DOE<00 O.DOE<00 O.DOE<00 O.DOE<00 I.OOE-02 O.DOE<00 0.DOE<00 0.DOE<00 Cs-134 7.53E<02 6,22E-02 2.59E-03 1.2 IE-OI 1.2 IE-OI 1,48E-OI 2.34E-OI 2.07E-03 8. IOE-02 8. 10f-02 3.84E-OI Cs-135 8.40E<08 1.30E-02 5.35E-04 1.13E-OZ 6.6IE-03 1.12E-02 1.30E-02 5.35E-04 I. 13E-02 6.61E-03 I. 12E-02 Cs-136 f 1.31 <01 6.5 IE-03 2.92E-03 1.85E-02 1.85E-02 2.57E-02 2.35E-02 2.27E-03 4. I BE-02 4. I BE-02 6.46E-02 Cs-137 I. I DE<04 7.97E-02 2. IIE-03 7.14E-02 7.14E-02 1.09E-OI 3.27E-OI 1.96E-03 4.62E-02 4.62E-02 3.13E-OI Cs-138 2.24E-02 5.52E-OZ 4.65E-IO 5.40E-05 5.40E-05 1.09E-04 2.28E-04 1.46E-04 2.0IE-04 2.0IE-04 3.17E-04 Bal37m 1.77E-03 2.93E-07 2.87E-05 4.07E-OB 5.12E-07 5.29E-07 2.93E-07 2.87E-05 4.07E-OB 5.12E-07 5.29E-07 Ba-139 5.78E-02 9.70E-05 1.72E-04 2.84E-06 2.84E-06 6.91E-OB 4.14E-04 2.39E-02 1.20E-05 1.20E-05 2.21E-07 Ba-140 1.28E<01 2.03E-02 4.IBE-02 1.33E-03 1.33E-03 2.55E-05 8.3IE-02 4.2IE-02 4.85E-03 4.85E-03 7.28E-05 Ba-141 1.26E-02 4. 7 IE-05 2.22E-14 1.59E-06 1.59E~ 3.56E-OB 2.00E-04 1.14E-04 " 6. 5 I E-06 6. 5 I E-06 1,12E-07 Ba-142 7.43E-03 2. 13E-05 3.00E-23 1.34E-06 1.34E-06 2.19E-OB 8.74E-05 1.14E'-06 4.88E-06 4.88E-06 6.29E-OB La-140 1.68E<00 2.50E-06 9.25E-02 '.33E-07 3.33E-07 1.26E-06 I.OIE-05 9.84E-02 1.19E-06 1.19E-06 3.53E-06 La-142 6.42E-02 1.28E-07 4.25E-04 1.45E-OB 1.45E-OB 5.82E-OB 5.24E-07 3. 31E-02 5.23E-OB 5.23E-OB 1.67E-07 Ce-141 3.25E<OI 9.36E-06 2.42E-02 7.18E-07 7. I BE-07 6.33E-06 3.97E-05 2.47E-02 2.94E-06 2.94E-06 1.9QE-05 Ce-143 1.38E<00 1.65E-06 4.56E-02 1.35E-07 I . 35E-07 1.22E-03 6.99E-06 5.55E-02 5.49E-07 5.49E-07 3.79E-03 Ce-144 2.84E<02 4.88E-04 1.65E-OI 2.62E-05 2.62E-05 2.04E-04 '.08E-03, 1.70E-OI I.IIE-04 I.IIE-04 6.52E-04 Pr-143 1.36E <01 9.20E-06 4.03E-02 4.56E-07 4.56E-07 3.69E-06 3.93E-05 4.24E-02 1.95E-06 1.95E-06 I.IBE-05 Pr-144 1.20E-02 3.0IE-OB 4.33E-I5 1.53E-09 1.53E-09 1.25E-OB 1.29E-GI 8.59E-05 6,49E-09 6.49E-09 3.99E-OB Prl44m 5.00E-03 8.86E-OB 5.69E-04 5.14E-09 3.29E-06 9.58E-OB 8.86E-OB 5.69E-04 5. 14E-09 3.29E-06 9.58E-OB Nd-147 I.IOE<OI . 6.29E-06 3.49E-OZ 4. 35E-07 4.35E-07 7.27E-06 2.79E-05 3.58E-02 1.75E-06 1.75E-06 2.26E-05 Bn-147 9.57E<02 2.87E-05 I. 17E-02 5.38E-07 5.02E-05 1.02E-04 2,87E-05 I. 17E-02 5.38E-07 5.02E-05 1.02E-04 Rn-149 2.2 If<00 1.53E-06 4,85E-02 1.24E-07 1.24E-07 2.50E-07 1.53E-06 4,85E-02 1.24E-07 1.24E-07 2.50E-07 Sm-147 3.94E<13 3.20E-OI 4.26E-02 I.IBE-03 2.98f-02 2.20E-OI 3.20E-OI 4.26E-02 I . I BE-052. 98E-02 2.20E-OI Sm-151 3.37E<04 6,87E-05 4.85E-03 2.84E-06 2.84E-06 I.IBE-05 6,87E-05 4.85E-03 2.84E-06 2.84E-06 I . IBf-05 Sm-153 1.95E<00 7.90E-07 2.43E-02 6.13E-OB 6.13E-OB 7.6IE-07 7.90E-07 2.43E-OZ 6.13E-OB 6.13E-OB 7.6IE-07 Eu-155 1.74E<03 4.63E-05 9.70E-03 5.26E-06 5.26E-06 1.08%5 4.63E-05 9.70E-03 5.26$ -06 5.26E-06 I.OBE-05 Ta-182 I. 15E<02 1.72E-05 4.85E-02 8.75E-06 8.75E-06 6. 37E-'05 1.72E-05 4.85E-02 8.75E-06 8.75E-06 6,37E-05

TABLE 2.1 DOSE COHHITHENT FACTORS (REH)HICROCI) HALF-LIFE (Sheet 4 of 4) NUCLIDE (DAYS) ADULT CHILD BONE Gl 'lRACT THYROID TOTAL BODY LIVER BONE Gl TRACT TIIYROI8 TOTAL BODY LIVER I-187 9.96E-OI 1.03E-04 2.82E-02 3.0IE-05 3.0IE-05 8.6lf-05 4.29E-04 3.57E-02 I. 14E-04 I. 14E-04 2.54E-04 Pb-210 8.14Et03 2. IOEtOI 2.03E-02 t, 3.00E-OI 1.70Et00 1.40Et00 2.IOEtOI 2.03E-02 $,.00E-OI 1.70Et00 1.40Et00 Pb-212 4 '3E-OI 1.20E-OI 7.57E-02 5.22E-04 2.57E-03 5.85E-03 1.20E-OI 7.57E-02 5.22E-04 2.57E-03 5.85E-03 Pb-214 1.86E-02 3.03E-04 3. 14E-03 I.IBE-05 5.64E-05 2.97E-05 3.03E-04 3.14E-03 I. I BE-05 5.64E-05 2.97E-05 81-212 4.2!E-02 3.03E-04 5.90E-03 4.97E-05 1.26E-04 7.24E-05 3.03E-04 5.90E-03 4.97E-05 1.26E-04 7.24E-05 81-214 1.38E-02 $ .16E-05 3.18E-03 5.IIE-06 2.97E-05 1.58E-05 4.16E-05 3.IBE-03 5.IIE-06 2.97f-05 1.58E-05 Po-212 3.50E-I2 1.50E-33 9. 17E-13 3.48E-34 1.96E-I5 I.OBE-33 1.50E-33 9.17E-I3 3.48E-34 1.96E-I5 I.OBE-33 Po-214 1.89E-09 4.80E-I2 4.28E-IO 7.0IE-I4 1.30E-I2 3.35E-I3 4.80E-I2 4.28E-IO 7.0IE-I4 1.30E-I2 3.35E-I3 Po-216 1.74E-06 9.35E-07 3.68E-07 3.IIE-09 1.85E-OB 7.39E-OB 9.35E-07 3.68E-07 3. I I E-09 1,85E-OB 7.39E-OB Po-218 2.12E-03 9.60E-05 6.84E-04 1.54E-06 8.62E-06 I.IIE-05 9.60E-05 6.84E-04 1.64E-06 8.62E-06 I.IIE-09 Ra-224 3.66Et00 3.30Et00 6.60E-OI 8.32E-02 7.47E-02 8.90E-02 3.30E(00 6.60E-OI 8.32E-02 7.47E-02 8.90E-02 Ra-226 5.84Et05 4.30EtOI 3.30E-OI 5.90E-OI 3.40Et00 5.90E-OI 4.30Et01 3.30E-OI 5.90E-OI 3.40Et00 5 '0E-OI Ra-228 2.10Et03 2.IOE+Ol 7.14E-02 4.00E-01 1.70Et00 4.00f-OI 2.IOEtOI 7.14E-02 4.00E-OI 1.70Et00 4.00E-OI Ac-228 2.55E-OI 3.48E-03 8.07E-03 6.13E-06 1.99E-04 3.54E-04 3.4BE-03 8.07E-03 6. 13E-06 1.99E-04 3.54E-04 Th-228 6.98Et02 4.10ft00 4.70E-OI 7.42E-03 3.80E-02 2.34E-02 4.10Et00 4.70E-OI 7,42E-03 3.80E-02 2.34E-02 Th-230 2.8IEt07 1.60ftOI I.BOE-OI 4.56E-03 9.24f-02 2.IBE-02 1.60EtOI I.BOE-OI 4.56E-03 9.24E-02 2.IBE-02 Th-232 5.1IE+12 I.BOftOI 1.50E-OI 3.94E-03 9.63E-02 I.BBE-02 I.BOEt01 1.50E-OI 3.94E-03 9.63f-02 I.BBE-02 Th-234 2.4IEt01 4.91E-05 1.60E-OI 1.60E-06 6.39E-04 1.46E-05 4.9IE-05 1.60E-OI 1.60E-06 6,39E-04 1.46E-05 Pa-234 2.79E-OI 3.00E-04 I. I I E-02 7.20E-06 3.12E-04 2.28E-04 3.00E-04 I. I I E-02 7.20E-06 3.12E-04 2.28E-04 U-234 8.91ft07 3.10ftOI I.BOE-OI 6.32E-02 2.30Et00 6.32E-02 3.IOEtOI I.BOE-OI 6.32E-02 2.30ft00 6.32E-02, U-238 1.63E+12 2.80f t01 1.70E-OI 5;63E-02 2.00Et00 5.35E-02 2.80Etol 1.70E-OI 5.63E-02 2.00Et00 5.35E-02 Np-238 2.12Et00 4.42E-03 3.2IE-02 1.22E-05 4.03E-04 I.OBE-03 4.42E-03 '.2IE-02 1.22E-05 4.03E-04 I.OBE-03 Hp-239 2.35Et00 1.19E-06 2.40E-02 6.45E-OB 6.45E-OB I ~ 17E-07 5.25E-06 2.79E-02 2.65E-07 2.65E-07 3.77E-07 Pu-238 3.20Et04 2.10ft00 2.10E-OI 3.23E-03 2.83E-02 4.40E-OI 2.10Et00 2.IOE-OI 3.23E-03 2.83f-02 4.40E-OI Pu-239 8.80ft06 2.60Et00 2.00E-OI 3.63E-03 3. 13E-02 4.90E-OI 2.60Et00 2.00E-OI 3.63E-03 3. 13E-02 4.90E-OI Pu-240 2.39Et06 2.60Et00 2.00E-OI 3.62E-03 3.13E-02 4.90E-OI 2.60Et00 2.00E-OI 3.62E-03 3.13E-02 4.90E-OI Pu-241 5.37Et03 4.83E-02 9.92E-04 7.49E-05 6.19E-04 9.50E-03 4.83E-02 9.92E-04 7.49E-05 6.19E-04 9.50E-03 Pu-242 1.37Et08 2.60Et00 1.90E-OI 3.45E-O3 2.98f-02 4.70E-OI 2.60Et00 1.90E-OI 3.45E-03 2.98E-02 4.70E-OI Am-241 1.58Et05 B.OOEtOI 2.IOE-OI 1.20E-OI I.OOEt00 1.70ftOI B.OOEtOI 2.10E-OI 1.20E-OI 1.00Et00 1.70EtOI An-242 6 '8E-Ol 5.19E-03 9.26E-03 1.06E-05 1.44E-04 1.5IE-03 5.19E-03 9.26E-03 1.06E-05 1.44E-04 1.5IE-03 Am-243 2.69Et06 8.50Etol 2.20E-OI 1.30E-OI 1.00Et00 1.70EtOI 8.50EtOI 2.20)-01 1.30E-OI 1.00ft00 1.70EtOI Cm-242 1.63Et02 I. 50Et00 2.30E-OI 2.72E-03 2.5BE-02 4.40E-OI 1.50ft00 2.30E-OI 2.72E-03 2.5BE-02 4.40E-OI Cm-243 1.04ft04 4.80E tOI 2.50E-OI 8.22E-02 7.IOE-OI 1.20EtOI 6.00Et03 I.OOEt03 I.OIEt03 2.0IEt03 I.OOEt03 Cm-244 6.6IEt03 3.80EtOI 2.20E-OI 6.40E-02 5.60E-OI 9.30Et00 3.80EtOI 2.20E-OI 6.40E-02 5.60E-OI 9.30E-OO Dose factors were taken fran the follow lng references in or der of preferencet I. Regulatory Gu Ide I ~ 109, U SNRC, Obtob er 1977

2. NUREGlCR-0150 , D. E. Dunn ing', ORNL, October,1981

3. ORNLA992, G. G. Klllough and L. R. HcKay, Harch '

1976 g I

TABLE -2.2 FISH CONCENTRATION FACTORS~- (Page 1 of 2) NUCLIDE NUCLIDE NUCLIDE H-3 9.00E-O'1 Tc-99m 1.50E+01 Ce-144 1.DOE+00 C-1 4 4.60E+03 Ru-103 1.00E+Ol Pr-143 2.50E+01 Na-22 1.00E+02 Ru-105 1.00E+Ol Pr-144 2.50E+01 Ha-24 1.DOE+02 Ru-106 1.00E+01 Prl44m 2.50E+01 P-32 3.00E+03 Rh103m 1.00E+Ol Nd-147 2.50E+Ol Cr-51 2.00E+02 Rh-105 1.00E+01 Pm-147 2.50E+Ol Mn-54 4.00E+02 Rh105m 1.DOE+01 Pm-149 2.50E+01 Hn-56 4.DOE+02 Rh-106 1.00E+01 Sm-147 2.50F+01 Fe-55 1.DOE+02 AgllOm 2.31E+00 Sm-151 2.50F+01 Fe-59 1.00E+02. Ag-ill '2. 31E+00 Sm-153 2.50E+Ol Co-57 5.00E+01 Sb-122 1.DOE+00 E6-155 2.50E+01 Co-58 5.00E+01 Sb-124 1; OOE+00 Ta-182 3.DOE+04 Co-60 5.00E+01 Sb-127 1.00E+00 8-187 1.20E+03 N1-63 1.00E+02 Tel25m 4.DOE+02 Pr-210 3.00E+02 H1-65 1.DOE+02 Te-127 4.00E+02 Pb-212 3.DOE+02 Cu-64 5.00E+01 Tel27m 4.DOE+02 Pb-214 3.00E-02 Zn-65 2.00E+03 Te-129 4.DOE+02 B1-212 1.50E+01 Zn-69 2.00E+03 Tel29m 4.00E+02 B1-214 1.50E+01 As-74 1.00E+02 Te-131 4.00E+02 Po-212 5.00E+01 As-76 1.DOE+02 Tel3lm 4.00E+02 Po-214 5.00E+01 Br-83 4.20E+02 Te-132 4.00E+02 Po-216 5.00E+Ol Br-84 4.20E+02 I-1 29 1.50E+Ol Po-218 5.00F+01 Br-85 4.20E+02 1-130 1.50E+Ol Ra-224 5.00E+01-Kr-83m 1.00E+00 I-131 1.50F+Ol Ra-226 5.00E+01 Kr-85m 1.DOE+00 I-l32 1.50E+01 Ra-228 5. OOEi01 Kr-85 1.00E+00 I-133 1.50E+01 Ac-22A 2.50F+01 Rb-86 2.DOE+03 I-134 1.50E+01 Th-228 3.00E+01 Rb-88 2.00E+03 I-1 35 1.50E+01 Th-230 3.00F+01 Rb-89 2.00E+03 Xel33m 1.DOE+00 Th-232 3.00E+01 Sr-89 3.00E+01 Xe-133 1.00E+00 Th-234 3.00E+01 Sr-90 3.00E+01 Xel35m 1.00E+00 Pa-234 1.10E+Ol Sr-91 3.00E+01 Xe-135 1.00E+00 U-234 1.00E+Ol Sr-92 3.00E+Ol Cs-1 34 2.00E+03 U-238 1.00E+01 Y-90 2.50E+01 Cs-135 2.00E+03 Hp-238 1.00E+Ol Y-91 2.50E+Ol Cs-136 2.00E+03 Hp-239 1.00E+01 Y-91m 2.50E+Ol Cs-137 2.00E+03 PU-238 3.50E+02 Y-92 2.50E+01 Cs-138 2.00E+03 PU-239 3.50E+02 Y-93 2.50E+01 Ba137m 4.00E+00 Pu-240 3.50E+02 Zr-95 3.33E+00 Ba-139 4.00E+00 Pu-241 3.50E+02 Zr-97 3.33E+00 Ba-140 4.00E+00 PU-242 3.50E+02 Hb-95 3.00E+04 Ba-141 4.00E+00 Am-241 2.50E+01 Nb-95m 3.00E+04 Ba-142 4.DOE+00 Am-247 2.50E+01 Nb-97 3.00E+04 La-140 2.50E+01 Am-243 2.50E+01

TABLE 2.2 FISH CONCENTRATION FACTORS' (Page 2 of 2) NUCLIDE NUCLIDE NUCLIDE Nb-97m 3.00E+04 La-1 42 2.50E+Ol C01-242 '2. 50E+01 Ho-99 1.00E+Ol Ce-141 1.00EHO Cm-243 2.50E+01 Tc-99 1.50E+Ol Ce-143 1.DOE+00 Cm-244 2.50E+01 PThe source for the fish concentration factors, given in order of preference 15: NUREG/CR-1336, "The Bioaccumulation Factor for Phosphorus-32 in Edible Fish Tissue," B. Kahn and K. S. Turgeon, Georgia Institute of Technology, . March 1980. Regulatory Guide 1.109, October 1977. UCRL-50564, "Concentration Factors of Chemical Elements in Edible Aquatic Organisms," S. E. Thompson, et al.; Lawrence Livermore Laboratory, October 1972. UCRL-50163, "Prediction of the Maximum Dosage to Han from the Fallout of Nuclear Devices: IV. Handbook for Estimating the Maximum Internal Dose from Radionuclides Released to the Biosphere," Y. C. Ng, et al.; Lawrence Livermore Laboratory, Hay 1968. Guide 1.109, Draft, Harcy 1976. t'egulatory TVA generated numbers for noble gases.

0 TABLE .3 RECREATION DOSE FACTORS (Sheet I af 4) NUCLIDE SMIHHING SIIORELINE (HREHJYEAR PER UCI IHL) (HREH[YEAR PER UCI ISQUARE CENTIHETER) BONE Gl TRACT THYROID TB LIVER SKIN BONE Gl TRACT TIIYROID 18 LIVER SKIN 11-3 0.00EEM O.OOE~ 0.00ft00 O.OOEc00 0,00E F00 O.ME <M O,DOE F00 0.00ft00 O.ME~00 0.00Es00 O.OOEi00 O.ME~00 C-I4 O.OOE~ O.ME~ O.ME F00 O.OOE<M O.OOE F00 O.OOEIM 0.00fi00 O.MEUM O.ME tM O.OOEt00 O.Mft00 0.00ft00 Na-22 3.14f<07 2.49E&7 2.30E&7 2.67E407 2.27E&7 3.16E+07 2.76fi06 2. 19E<06 2.0lft06 2.33Et06 1.99ft06 2.76ft06 Ne-24 5.66EE07 5.92ft07 6.22ft07 5.39E<07 4.80E<07 6.16E(07 3.96E>06 4.IOE(06 4.28ft06 3.76fo06 3.33E<06 4.29ft06 P-32 0.00E F00 0.00ft00 0.00f tM 0.00EIM O.Mft00 O.Mft00 0,00ft00 O.Mfc00 0.00ft00 0,00f<00 0.00E<00 0.00ft00 Cr-51 5.43fw05 3.07&05 3.38005 3.79E<05 3.09E&5 4.56ft05 5.45ft04 3.08ft04 3.39fo04 3.8lfc04 3.IOE<04 4.69fc04 Hn-54 I. 16E F07 8.57E<06 7.35Et06 9.68ft06 8.26E407 1.24ft06 1.04fi05 7.69ft05 6.60E405 8.69ft05 7.42E+05 I. I If<06 Hn-56 2. 33EA7 2. 14&07 I.82E<07 2.07ft07 I.BIE<07 2.54E<07 1.88E<06 1.69E ~ I.44fi06 1.66ftP6 1.45E~06 2.05E<06 Fe-55 3.16fiOI 3.47f A I 6.94E<00 1.68ft02 !.47E-OI 3.16E<03 2.7lfsOI 2.98E<01 5.96E~00 1.44ft02 1.26E-OI 2.71403 Fe-59 1.64E<07 1.38ft07 1.23EA7 1.45ft07 1.23fo07 1.76E&7 1,36ft06 I . 15E 106 1.02ft06 1.20ft06 1.02ft06 1.46fi06 Co-57 2. 71 f<06 9.80E405 1.69Et06 1.48fc06 1.13fe06 1.75E~06 2.82E<05 1.02ft05 1,76E<05 1.55E>05 1.17ft05 1.94E405 Co-58 1.38E>07 1.03ft07 8.78ft06 1.13ft07 9.68E<06 1.43E&7 1.25EI06 9.36ft05 8.00fc05 1.03ft06 8.82ft05 1.30ft06 Co-60 3.46ft07 3.02EA7 2. 73E F07 3. f I I F07 2.62E<07 3.67E407 2.83fi06 2.46fc06 2.23ft06 2.54fi06 2.14E<06 3.00ft06 Ni-63 0.00ft00 0.00ftM 0.00E 100 0.00E F00 0.00ft00 0.00ft00 O.ME.<00 0,00EEOO O.ME<00 O.OOEcM O.OOEi00 0.00E<00 Nl-65 7.65ft06 6.86E<06 6.50ft06 6.94E<06 5.84ft06 7.93fi06 6.18E(05 5.52ft05 5.22fo05 5.60fs05 4.7lft05 ~ 6.41E<05 Cu-64 2.83E~O6 2.20E<06 I.85ft06 2.23EA5 1.92E<06 2.67E>06 2.71Ei05 2.1lft05 1.78ft05 2. 14EE05 1.84E)05 2.59E<05 Zn<5 7.99Et06 6.49E~ 5.58E<06 6.96ft06 5.90E<06 8.67E<06 6.75E<05 5.48ft05 4.7IE<05 5.88ft05 4.98ft05 7.40E&5 Zn-69 9.55E A I 6.49ftOI 6.09EIO I 7. 12001 6.00ftOI 8.5IE<OI 9.40EIOO 6.39fo00 6.00E %0 7.DIE<00 5.90ftM 8. 38E F00 As-74 1.70ft05 1.30E<05 1.40E+05 1.40E&5 I, IOE i05 1.60ft05 1.36ft06 I.IOft06 I . 16E+06 1.12ft06 9.40E<05 1.33E<06 As-76 8. 3 I f%4 6.68ft04 7,04E&4 6.83ft04 5.73E~04 8.12E<04 6.82fs05 5.48E405 5.78E&3 5.60E<05 4.70Et05 6.66ft05 Br-83 1.12EA5 8.64E&4 7.24ft04 8,8lft04 7.59fi04 1.06E<05 1.07E<04 8.29EI03 6.95E<03 8.45E>03 7.28ft03 I.02E>04 Br-84 2.46E>07 2.42&07 2.59ft07 2.28ft07 2.03ft07 2.69ft07 1.80ft06 1.73E<06 1.79&06 1.65ft06 1.46EAS 1.96ft06 Br-85 2.86ft05 2.1lft05 I.BIE>05 2.39E<05 2.04E405 3.07fc05 2.55fc04 1.88ft04 1.61ft04 2. 13EA4 1.82ft04 2.74E<04,-. Kr-83m 5.24ft02 1.22E<02 1.22E>02 9.46E>02 3.7IE>01 I. 13ft04 4.33fi02 I.IBEt02 5.97ftOI 9.66E<02 I 12ftOI

                                                                                                                                        ~        1.23fc04 Kr-85m 3.2IE<06 1.36M%         1.97ft06    I.93ft06 1.50ft06           2.30E<06           3.30fi05  1.39ft05 2.02ft05 1.99Et05         1.54Et05   2. 39E A5 Kr-85 3.34ft04 2.59ft04       2. 17ft04    2.62ft04        2.26E<04    3.14E<04           3.22E(03 2.49ft03 2.09E<03 2.53fc03          2.IBE<03   3.03E<03 Rb-86    1.29EAS     1.04E~ 8.73ft05        I. 12ft06 9.50E&5          1.42E<06           I.IOft05 8.79ft04 7.40E404 9.50fc04          8.06E<04   1,20fi05 Rb-88   8.99E t06   9.16ft06 8.10ft06 8.32ft06 7.33E<06                9.90E<06           6.77fi05 6.82E<05     5.97fi05 6.24ft05      5.49E<05   7.46ft05 Rb-89   2.89ft07 2.67E<07 2.4lf&7 2.61ft07 2.27E&7 3.17ft07                               2.27E>06  2.06E>06    I.85E>06     2.04E~06  1.77E>06   2.49E>06 Br-89    I .BBEA3    1.4lft03  I.IBE<03     1.58ft03       1.35E&3     2.05E<03           1.66ft02  1.24ft02, 1.04ft02 1.40E<02        1.19ft02   I.BIft02 Sr-90   0. DOE IOO 0.00E~     0.00E>00     0.00MS 0.00ft00 0.00ft00                       0.00ft00  O.ME<00 O.Mft00 O.OOE>00           O.DOE<00   0.00ft00 Sr-91   9.7 E~ 7. 32E+06 1                6.32EAS      8.17ft06 6.96E de           1.04E407           8.56ft05  6.43ft05 5.56ft05 . 7.19E+05       6.13E&5 9.13ft05 Sr-92    1.86E&7 1.68E+07      1.59ft07    1.70E&7         1.43E<07    1.93ft07,.         1.50fo05  I . 35E8%   1.28E>06     1.37E<06  1.15ft06 1.55E<06 Y-90     I. IOE~    2.90E-OI   I.IIE-OI    1.32E+00        2.77E-02    1.06E tOI i        7.97E-OI  2. 17E-Ol 7.68E-02 9.65E-OI        1.9IE-02   7.87E<00 Y-91    4.99M)4 4.25EA4       3.77E&4      4.43ft04 l 3.75ft04         5. 33EA4           4. 12ft03 3.5 If&3 3. IIE<03 3.66Et03        3.10E>03   4.4IE403
                                                      ~
                                                        )

TABLE 2.3 RECREATION DOSE FACTORS (Sheet 2 of 4) NUCLIDE SWIHHING SIIORELINE (HREHI YEAR PER UC 1!HO (HREHIYEAR PER UCI) SQUARE CENT IHETER) BONE Gl TRACT TIIYROID TB LIVER SKIN BONE Gl TRACT TIIYROID TB LIVER SKIN Y-9IH 7.83Et06 6.02Et06 5.06Et06 ,6. 2 I Et 06 5.34Et06 7.53Et06 7.48Et05 5.74ft05 4.83F,t05 5.93Et05 5.10Et05 7.20Et05 Y-92 3.51ft06 2.80Et06 2.49Et06 3.02Et06 2.57Et06 3.72Et06 3.02E<05 2.39Et05 2. 12fi05 2.59Et05 2.20ft05 3. 19Et 05 Y-93 1.30Et06 I. IOE t06 9.9IEt05 I.IOE+06 9.42Et05 1.33Et06 I.IOEt05 8.9IEt04 8.17Et04 9.13Et04 7.77Et04 I. IOEt05 Zr-95 1.04Et07 7.78Et06 6.64Et06 8.56ft06 7.32Et06 I.OOEt07 9.56Et05 7.13Et05 6.08Et05 7.84Et05 6.7IEt05 9.88Et05 Zr-97 2.57ft06 2.P4ft06 1.87Et06 2. 18Et06 1.86Et06 2.62Et06 2.23ft05 1,74Et03 1.60Et05 1.88Et05 1.60Et05 2.27Et05 Nb-95 1.08ft07 B.0 Ift06 6.84Et06 8.87Et06 7.59Et06 I . 12E't 07 9.82Et05 7.31Et05 6.24ft05 8.09Et05 6.92Et05 1.02Et06 Nb-95m 1.17Et06 5.59Et05 7.04Et05 7.59Et05 5.90Et05 9.5IEt05 1.22Et05 5.66Et04 7.17ft04 8.05Et04 5.98Et04 1.23Et05 Nb-97 9.40E t06 7. I Ift06 6.03ft06 7.6lft06 6.52Et06 9.43Et06 8.77Et05 6.63Et05 5.62Et05 7.IOEt05 6.08Et05 8.79Et05 Nb-97m 1.03Et07 7.67E+06 6,54E+06 8.44Et06 7.22Et06 1.06Et07 9.42Et05 7.03ft05 5.99Et05 7.73ft05 6.6IEt05 9.74Et05 Ho-99 2.4IEt06 1.63Et06 1.52Et06 1.87Et06 1.57Et06 2.34ft06 2,27Et05 1.51Et05 1.43Et05 1.75ft05 1.47Et05 2.2IEt05 Tc-99 0.00Et00 0.00ftOO 0.00ftOO 0.00Et00 O.OOEt00 O.OOEt00 O.OOEt00 O.OOEt00 0,00Et00 0.00Et00 O.OOEt00 0,00ft00 Tc-99m 2.74ft06 1.03ft06 1.69ft06 1.55ft06 I ~ 18Et06 1.83Et06 2.83Et05 1.07Et05 1.74Et05 1.60Et05 1.2IEt05 1.93Et05 Ru-103 7.05Et06 5.44Et06 4.57Et06 5.51ft06 4.75Et06 6.60Et06 6.8IEt05 5.25Et05 4.4IEt05 5. 32Et05 4.58Et05 6.37Et05 Tc-99 O.OOEt00 0.00ft00 O.OOEt00 O.OOEt00 0.00Et00 0.00Et00 O.OOEt00 0.00Et00 O.OOEt00 0.00Et00 O.OOEt00 O.OOEt00 Tc-99m 2.74Et06 1.03ft06 1.69Et06 1.55ft06 I.IBEt06 1.83Et06 2.83Et05 1.07Et05 1.74Et05 1.60Et06 1.2IEt05 1.93Et05 Ru-103 7.05Et06 5.44ft06 4.57Et06 5. 51 ft06 4.75Et06 6.60Et06 6,8IEt05 5.25ft05 4.4lft05 5.32Et05 4.58Et05 6.37Et05 Ru-105 1.15Et07 8.32Et06 7.34Et06 9.16Et06 7.79Et06 1.14Et07 1.08Et06 7.78Et05 6.88Et05 8.57Et05 7.29Et05 1.06Et06 Ru-106 0.00EtOO 0.00ftOO 0.00ftOO 0.00Et00 O.OOEt00 O.OOEt00 O.OOEt00 O.OOEtOO O.OOEt00 0.00Et00 O.OOEt00 O.OOEt00 Rhl03m 3.73Et03 4.88Et02 1.27Et03 2.82Et03 3.92Et02 1.27Et04 1.74Et03 2.IOEt02 5.66Et02 1.36Et03 1.63Et02 6.42ft03 Rh-105 1.35Et06 7.56Et05 8.38Et05 9.39ft05 7.64Et05 1.12Et06 1.36Et05 7.59Et04 8.4IEt04 9.43Et04 7.67Et04 1.13Et05 Rht05m 6.12Et05 2.18Et05 3.75Et05 3.42Et05 2.5IEt05 4.5IEt05 7.05Et04 2. 30Et04 4, IOEt04 4. IIEt04 2.66Et04 7. 39Et04 Rh-106 2.99E+06 2.30ft06 1.96Et06 2.4IEt06 2.07Et06 2.93ft06 2.8IEt05 2.16Et05 1.84&65 2.25Et05 1.94Et05 2.74Et05 AgllOm 3.87Et07 2.97Et07 2.68Et07 3.28Et07 2.79Et07 4.03Et07 3.4IEt06 2.61Et06 2:35Et06 2.88Et06 2.45Et06 3.55ft06 Ag-III 4.03ft05 2.32Et05 2.5IEt05 2.63Et05 2.31Et05 3.39Et05 4.03Et04 2.32Et04 2.51Et04 2.83Et04 2.3IEt04 3. 39Et04 Sb-122 8.06Et04 6.27Et04 6.58E+04 6.3IEt04 5.26Et04 7.73Et04 6.83Et05 5.3IEt05 5.57Et05 5.35Et05 4.46Et05 6.54Et05 Sb-124 2.6lft07 2.28Et07 2.07Et07 2.29Et07 1.98Et07 2.7IEt07 2.18Et06 1.86Et06 1.69Et06 1.90Et06 1.64Et06 2.25Et06 Sb-127 I.OIEt07 7.39Et06 6.47Et06 8.03Et06 6.85Et06 9.91Et06 9.52EI05 6.94Et05 6.09Et05 7.55Et05 6.43Et05 9.3IEt05 Tel25m 2.47E+05 2.93Et04 1.24ft05 1.35ft05 4.71ft04 3.39Et05 4.60Et04 9.08Et03 2.32Et04 2.50Et04 8.75Et03 6.29Et04 Te-127 7.84Et04 5.17Et04 4.98Et04 5.77Et04 4,83Et04 6,89Et04 7.74Et03 5.10Et03 4.92Et03 5.69Et03 4.77Et03 6 '0Et03 Te 127m 6.9lft04 1.33ft04 3.45Et04 3.82Et04 1.28Et04 9.89Et04 1.3IEt04 2.54ftO) 6,60Et03 7.2IEt03 2.44Et03 1.86ft04 Te-129 8.68Et05 6.12Et05 5.58Et05 6.69Et05 5.60Et05 8;33ft05 8.52Et04 5.87Et04 5.43Et04 6.50Et04 5.37Et04 8.28Et04 Tel29m 4.73Et05 3.23ft05 2.94Et05 3.71Et05 3.02Et05 5.03Et05 4.89Et04 3.09Et04 2.98Et04. 3.7IEt04 2.MEt04 5.38Et04 Te-131 6.79ft06 4.2lft06 4.37Et06 4.99ft06 4.13Et06 6.IIEt06 6.49Et05 3.94Et05 4.16Et05 4.7IEt05 3.88Et05 5.78Et05 Te I 31m 2.06Et07 1.53E t07 1.39Et07 1.70Et07 1.45ft07 2.12Et07, 1.84Et06 1.35ft06 1.23Et06 .1.5IEt05 1.28Et06 1.89Et06 Te-132 4.27ft06 1.92Et06 2.54Et06 2.68ft06 ,2.04Et06 3.32Et06 4.55Et05 1.98Et05 2.68Et05 2.83Et05 2.12Et05 3.60Et05 1-129 2.25Et05 4.84Et04 1,19Et05 I ~ 15Et05i 4.75Et04 2.49Et05 5.02Et04 1.07Et04 2.67ft04 2.57Et04 1.05Et04 5.70Et04 I I

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T 2.3 RECREATION DOSE FACTORS (Sheet 3 of 4) NUCLIDE SMIHHING SIIORELINE (HREH)YEAR PER UCIJHL) NREHI YEAR PER UCI )SQUARE CENTIHETER) BONE Gl TRACT TIIYROID TB 'IVER SKIN BONE Gl TRACT TIIYROID TB LIVER SKIN 1-130 3.09E<07 2.33E<07 2'DOE<07 x2'50E<07 2'14E<07 3.08E<07 2.80E<06 2.17E<06 1.86/<06 2. 32E106 1.99E<06 2.86E<06 1-131 6.22E <06 3.93E<06 3.92E<06 '.54E<06 3.77E<06 5.47E<06 6.16E<05 3.87E<05 3.88E<05 4.49E<05 3.72E<05 5.4IE<05 1-132 3.23E<07 2.45E<07 2.16E<07 2.68E<07 2.29E<07 3.32E<07 2.9lf<06 2.20f<06 1.93E<06 2.4 I E<06 2.06E<06 2.99E<06 ~ 1-133 8.96E<06 6.90E<06 5.89E<06 7.18E<06 6.16E<06 8.69E<06 8.44E<05 6.49E<05 5.54E<05 6.75E<05 5.79E<05 8.17E<05 1-134 3.67E<07 2.P4E<07 2.49E<07 3.1lf<07 2.65E<07 3.89E<07 3.22E<06 2.46E<06 2.16E<06 2.7IE<06 2.32E<06 3.40E<06 1-135 2. 19E<07 1.95E<07 1.75E<07 1.96E<07 1.67E<07 2.33E<07 1.78E<06 .1.57E<06 1.4IE<06 1.58E<06 1.35E<06 1.89E<06 Xol33m 6.05E<05 2.38E<05 3.55E<05 3.7IE<05 2.6lf<05 5.27E<05 8.09E<04 2.8IE<04 4.65E<04 4.77E<04 3.05E<04 7.7IE<04 Xe-133 8.52E<05 2.53E<05 4.84E<05 4.24E+05 2.74E<05 5.73E<05 I.IIE<05 3.17E<04 6.28E<04 5.57E<04 3.39E<04 8.27E<04 Xo 135m 6.4IE<06 4.94E<06 4. 15E<06 5.04E+06 4.33E<06 6.08E<06 6.2IE<05 4.75E<05 4.DIE<05 4.87E<05 4.17E<05 5.90E<05 Xo 135 4.54E<06 2.28E+06 2.76E<06 3.02E<06 2.40E<06 3.63E<06 4.59fi05 2.29E<05 2.79E<05 3.04E<05 2 '1E<05 3.67E<05 Cs-134 2.22E<07 1.67E+07 1.43E<07 I.BIE<07 1.55E<07 2.26E<07 2.04E<06 I ~ 54E<06 1.32E<06 1.67E<06 1.43E<06 2.08E<06 Cs-135 O.DOE<00 O.DOE<00 0.DOE<00 O.OOE<00 0.DOE<00 0.00E<00 0.00E<00 O.OOE<00 O.OOE<00 0.DOE<00 O.DOE<00 O.DOE<00 Cs-136 3.!DE<07 2.26E<07 2.03E<07 2.55E<07 2. 15E<07 3.2IE<07 2.77E<06 2.DOE<06 I.BIE<06 2,26E<06 1.9IE<06 2.85E<06 Cs-137 0.DOE<00 0.DOE<00 O.DOE<00 0.DOE<00 0.DOE<00 O.OOE<00 O.DOE<00 O.OOE<00 O.DOE<00 0.DOE<00 0.DOE<00 0.DOE<00 Cs-138 3.29E<07 3.03E<07 2.86E<07 2.98E<07 2.56E<07 3.46E<07 2.62E<06 2.37E<06 2.23E<06 2.35E<06 2.02E<06 2.74E<06 Bn137m 8.56E<06 6.45E<06 5.48E<06 6.92E<06 5.93E<06 8.59E<06 B.DIE<05 6.02E<05 5.12E<05 6 47E<05 5.54E<05 8.04E<05 Bn-139 7.49E<05 3.44E<05 4.73E<05 4.66E<05 3.60E<05 5.55E<05 7 'IE>04 3.38f<04 4.75E<04 4.67E<04 3.57E<04 5.62E<04 Ba-140 2.29E<06 1.60E+06 1.46E<06 1.73E<06 1.46E<06 2,10E<06 2.29E<05 1.56E<05 1.46E<05 1.7IE<05 1.42E<05 2.13E<05 Ba-141 1.3IE<07 8.90E<06 8.96E<06 1.02E<07 8.49E<06 1.22E<07 1.21E<06 7.97E<05 8.15E<05 9.26E<05 7.70E<05 I. 12E<06 Bn-142 1.5IE<07 I. Ilf<07 1.02E<07 1.24E<07 1.04E<07 1.54E<07 1.34E<06 9.30E<05 9.03E<05 I.IOE<06 9. 17E<05 I. 36E<06 La-140 3.20E<07 2.91E<07 2.73E<07 2.88E<07 2.46E<07 3.31E<07 2.60E<06 2.32E<06 2.18E<06 2.32E(06 1.98E<06 2.67E<06 La-142 3.74E<07 3.80E+07 3.72E+07 3.47E<07 3.10E<07 4.10E<07 2.75E<06 2.73E<06 2.64E<06 2.53E<06 2.52E<06 3.DOE<06 Co-141 1.59E<06 5.94E<05 9.70E<05 9.DIE<05 6.75E<05 1.09E<06 1.69E<05 6.20E<04 1.02E<05 9.52E<04 7.07E<04 I. 16E<05. Ce-143 4.54E<05 2.64E<06 2.79E<06 3.22E<06 2.60E<06 4.DOE<06 4.66E<05 2.6IE<05 2.83E<05 3.24E<05 2.57E<05 4.07E<05 La-142 3.74E<07 3,80E<07 3.72E<07 3.47E<07 3.10E<07 4.10E<07 2.75E<06 2.73E<06 2.64E<06 2.53fi06 2.52E<06 3.DOE<06 Ce-141 1.59E<06 5.94E<05 9.70E<05 9.0IE<05 6.75E<05 1.07E<06 1.69E<05 6.20E<04 1.02E<05 9.52E<04 7.07E<04 1,16E<05 Co-143 4.54E<05 2.64E<06 2.79E<06 3.22E<06 2,60E<06 4.DOE<06 4.66E<05 2.6IE<05 2.83E<05 3.24E<05 2.57E<05 4.07EI05 Co-144 4.18E<05 1.42E<05 2.5IE<05 2.26E<05 1.63E<05 2.DIE<05 4.64E<04 1.55ft04 2.76E<04 2.50E<04 1.76E<04 3.18E<04 Pr-143 1.26E-OI 9.38E-02 B.OOE-02 1.03E-OI 8.83E-02 1.30E-OI 1.15E-02 8.60E-03 7.33E-03 9.45E-03 8.09E-03 1.19E-02 Pr-144 4.40E-05 4.24E<05 3.74E<05 3.97E<05 3.50E<05 4.75E<05 3.46E<04 3.24E<04 2.87E<04 3.IOE<04 2.72E<04 3.7IE<04 Prl44H 1.42E<05 3.32E<04 7,19E<04 6.95E<04 '3.23E<04 1.25E.<05 2.28E<04 5.33E<0$ 1.15E<04 1.12E<04 5.17E<03 2.06E<04 Nd-147 2.33E<06 1.34E<06 1,44E<06 1.57E<06 1.25f<06 1.93f <06 2.47E<05 1.35E<05 1.50E<05 ~ 1.62E<05 1.27E<05 2.03E<05 Pm-147 7.86E<01 2.76E<01 4,92E<01 4.26E<01 3.23E<01 4.93E<OI 8. 17E<00 2.92E<00 5.IIE+00 4.43E<00 3.36E<00 5.17E<00 Pm-149 1.98E<05 1.12E<05 I. 23E<05 1.39E<05 1.13f<05 1.69E<05 1.98E<04 I.IIE<04 1.22E<04 I ~ 38E<04 1.12E<04 1.67E<04 Sm-147 O.DOE<00 0.DOE+00 O.DOE<00 O.DOE<00 0.DOE<00 O.OOE<00 .. O.DOE<DO 0.DOE<00 0.00E<00 0.00E<00 0.DOE<00 O.OOE<00 Sm-151 1.69E<OI 2.20E<00 5.68E<00 1.33E<01 1.6IE<00 6.78E<01 7.60E<00 '.04f<00 2.56E<00 6.24E<00 7.22E-OI 3.55E<01

T LE 2.3 RECREATIQN OOSE FACTORS (Sheet 4 ot 4) NUCLIDE SMIHHING SIIORELINE (HREHIYEAR PER UCIIHL) (HREHJYEAR PER UCI (SQUARE CENTIMETER) I BONE Gl TRACT THYROID TB LIVER SKIN G I TRACT TIIYROI0 TB LIVER SKIN Sm-153 1.25Et06 3.89Et05 7.2IE<<05 6.33ft05 4.25E<<05 8.08E<<05 1.57Et05 4.7IE<<04 8.7Iif<<04 7.83Et04 5.07E<<04 I.Q4E<<05 Eu-155 1.35E<<06 4.28Et05 7.98E+05" 6.8IE<<05 4.78E<<05 8.2IEt05 1.54Et05 4.82Et04 8.98E<<04 7.73Et04 5.35E<<04 9.49E<<04 1 Ta-182 2.42Et05 1.90Et05 I.BOE<<05 2.04E<<06 1.68E<<05 2.44ft05 1.94E<<06 1.4IE<<06 1.45E<<06 1.63E<<06 1.35Et06 1.96E<<06 M-187 7.25ft06 5.09E<<06 4.57ft06 5.55E<<06 4.68f<<06 6.8IEt06 6.99E<<05 4.84E<<05 4.39f<<05 5.30Et05 4.45Et05 6.52Et05 Pb-210 3.69Et04 9175Et03 1.7IEt04 1.76E<<04 9.16Et03 3.27E<<04 5.3IE<<03 1,46E<<03 2.42E<<03 3.05Et03 1.28Et03 1.43E<<04 Pb-212 2.89E<<06 1.26E<<06 1.72E<<06 I;78Et06 1.36Et06 2. 13Et06 2.99E<<05 1.29E<<05 1.78Et05 1.83Et05 1.40Et05 2.25E<<05 Pb-214 4.29E<<06 2.39Et06 2.65E<<06 2.95E<<06 2.39E<<06 3.55Et06 4.32fi05 2.39Et05 2.66E<<05 2.96fi05 2.39Et05 3.6IE<<05 Bl -21 Z 2.59E<<06 Bi-214 2. IOE<<07 2.08Et06 1.89Et07 1.89E<<06 1.69E<<07 2.22'E<<06 1.87Et07 1.90E<<06 1.62f<<07 2.69Et06 2.23E<<07 'ONE 2.25E<<05 1.7IEt06 1.78Et05 1.5IE<<06 1.6IE<<05 1.35E<<06 1.92E<<05 1.5IE<<06 1.63E<<05 1.3IEt06 2.36Et05 I.BIE<<06 Po-212 O.OOE<<00 O.OOEt00 O.OOE<<00 O.OOEt00 Q.OOEt00 O.OOE<<00 O.OOE<<00 O.OOE<<00 0.00Et00 O.OOEtOO O.OOE<<00 O.OOE<<00 Po-214 1.54E<<03 I. 14E<<03 9.75E<<02 1.27F<<03 1.09Et03 1.62Ei03 1.39E<<02 1.03E<<02 8,84E<<01 1.15E<<02 9.85E<<01 1.46Et02 Po-216 0.00f<<00 O.QOE<<00 0.00E<<OQ Q.OQE<<00 Q,OOE<<00 O.OOE<<00 O.OOEt00 O.OOE<<00 O.OOE<<00 O.QOE<<00 O.OQEt00 O.OOE<<00 Po-218 O.OQE<<00 O.OOEt00 O.OOE<<00 O.QQE<<00 O.OOE<<00 O.QOE<<QO O.OOE<<00 O.OOE<<00 O.OOEt00 O.OOE<<00 O.OOEtOO O.OOEt00 Ra-224 1.87E<<05 8.92E<<04 1.13Et05 1.2IE<<05 9.45E<<Q4 1.45EtQ5 1.9OE<<04 9,04E<<03 1.15Et04 1.22Et04 9 58E<<03 1.49Et04 Ra-226 1.37E<<05 5.79E<<04 8.19Et04 8.2IEt04 6.26E<<04 9.83E<<04 1.41E<<04 5.94Et03 8.4IE<<03 8.45E<<03 6,4IE<<03 1.05Ei04 Ra-228 8.53E-05 9.39E-05 1.88E-05 4.53E-04 3.98E-07 8.53E-03 7.89E-05 8.68E-05 1.74E-05 4.19E-04 3.68E-07 7.89E-03 Ac-228 1.32E<<07 9.95ft06 8.99E<<06 I.IOEt07 9.30E<<06 1.37E<<07 I. 17E<<06 8.65E<<05 7.86Et05 9.64F<<05 8.14E<<05 1,23E<<06 Th-228 4. 33E<< 04 1.54E<<04 2.56Et04 2.4IE<<04 1.74E<<04 3.33Et04 4.75Et03 1.67E<<03 2.74Et03 2.95ft03 1.84E<<03 8.88ft03 Th-230 8. 79M)3 2.86E<<03 4.78E<<03 4.83E<<03 3.07E<<03 I.OQE<<04 I.IIE<<03 3.53Et02 5.44Et02 6.92E<<02 3.39E<<02 5.86E<<03 Th-232 3.91 E<<03 1.20E<<03 2.03E<<03 2.2IE<<03 1.23E<<03 6.8IE<<03 5.93Et02 1.78Et02 2.53E<<02 6.IOEt02 1.45E<<Q2 5.44E<<03 Th-234 1.90E<<05 6.00E<<04 I.IOE<<05 9.53E<<04 6.63E<<04 I.IBEt05 2.14f<<04 6.70Et03 1.23Et04 I.IIE<<04 7.33E<<03 1.94E<<04 Pa-234 2.89E<<07 2.07E<<07 1.92E<<07 2.34Et07 1.98E<<07 2.93Et07 2.6IE<<06 1.83Et06 1.72Et06 2.IOEt06 1.77Et06 2.69Et06 U-234 2.77Et03 8.3QE<<02 1.38E<<03 I.BOE<<03 8.36Et02 8.05E<<03 5.7IE<<02 1.46f<<02 1.85E<<02 7.43E<<02 I.OOE<<02 7.34E<<03 U-238 9.69E<<02 2.47Et02 3.66E<<02 B.OZEt02 1.97Et02 5.9IE<<03 3.32E<<02 8.4IEtOI 7.05EtOI 5.46Et02 2.97E<<01 6.06E<<03 Hp-2'$8 7.50Et06 5.78E<<06 4.77Et06 6.38ft06 5,43Et06 8.32Et06 6.50E<05 4.99Et05 4.12E<<05 5.54E<<05 4.69ft05 7.45f <05 Np-239 3.44E<<06 1.40E<<06 2. 14ft06 2.0ZE<<06 1.57E<<06 2.43Et06 3.59E<<05 1.45E<<05 2.22E<<05 2.13Et05 1.62E<<05 2.90E<<05 Pu-238 9.79EtOZ 2.32E<<02 3.16E<<02 I.OOEt03 1.67Et02 8.46Et03 4.77E<<02 1.42E<<02 7.02E<<01 7,97E<<02 2.54E<<OI 8.55E<<03 Pu-239 1.39E<<03 4.5 IE<<02 7.98EtOZ 9.42ft02 5.05E<<02. 3.87Et03 2.83E<<02 8,55E<<01 9.52EtOI 3.60E<<02 5.44F<<OI 3.32Et03 Pu-240 I.0 IEt03 2.33E<<02 3.34EtQZ 9.90ftOZ 1.78Et02 8. IOE<<03 4.65Et02 1.36ft02 7,17E<<01 7.64Et02 2.69EtOI 8. 14Et03 Pu-241 O.OOEtQQ O.QOE<<00 Q.OOE<<00 O.OOE<<00 O.OOE<<00 O.OOE<<00 O.OOE<<00 O,OOE<<00, 0.00Et00 O.OOE<<00 O,QOEt00 O.OOEt00 Pu-242 8.25E<<02 1.93E<<02 2.83ft02 7.96Et02 1.52E<<02 6.40E<<03 3.68E<<02 6.23EtOI'.8IEt01 6,03Et02 2,22E<<01 6.41E<<03 An-241 5.0IEt05 1.43f<<05 2.47Et05 2.37E<<05 1.42E<<05 3.12E<<05 6.40Et04 I.BIEt04 3.IIEt04 3.16E<<04 1.79Et04

                                                                                                                   ~                     5.77Et04 An-242   3.08E<<05     1.04E<<05  1.95E<<05    1.62Et05   I.ZIEt05  1.96E<<05          3.32Et04    I.IIE<<04 2.07Et04 I.BOE<<04 I 29Et04        2.97E<<04 Am-243 1.22E<<06      3.7IE<<05  6.70E<<05    5.97Et05   3.96E<<05  7.28E<<05,          1.37E<<05   4. 16E<<04 7.49Et04 6.79Et04 4.42Et04        9.30E<<04 Gn-242. 1.08E<<03     2.95E<<02  2.97E<<02     I. 14Et03  1.56E<<02 9.49E<<Q3          6.QBE<<02   ,2.02E<<02   7. 14EtOI    9.05E<<02 2.57EtOI   9.0QE<<03 3  )NA                                                                               I   NIlN
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0 TABLE 2.4a PUBLIC MATER SUPPLY INFORMATION" 2020 TRM POPULATION MATER SUPPLY 294.0 '00 Browns Ferry Nuclear Plant 283.0 U. S. Plywood-Champion Paper 274.9 50 Mheeler Dam 259.6 14,100 Muscle Shoals 259.5 2,700 TVA-HFDC 254.3 21,100 Sheffield 245.0 520 Colbert Steam Plant 239.3 3,900 Cherokee 238.7 350 U.S. Steel Agri-Chemicals, Inc. gl 7.4 1 Yellow Creek Nuclear Plant 206.8 2.400 Hardin Co. Mater District 193.5 1,900 Tri-County Utility District 158.0 1,100 Cl i fton 101.9 170 Foote Mineral Co. 100.5 6,100 Hew Johnsonvi lie 100.4 13,300 Camden 100.0 375 Johnsonville Steam Plant 98.5 900 E. I. Dupont Company 95.5 700 Consolidated Aluminum Corporation 94.5 250 Inland Container Corporation 79.5 120 Bass Bay Resort 39.3 4,300 Jonathan Creek Mater District 28.5 9,100 North Harshall Mater District'rand 23.6 650 Rivers 17.8 600 B. F. Goodrich Chemical Co. 17.4 106 Airco Carbide 16.8 592 Airco Alloys 16.7 510 Air Products and Chemicals 1.1 69,800 Paducah

From TVA Mater guality Branch, updated December 1979

TABLE 2.4b FISH HARVEST OATA RIVER SPAN NAME OF REACH FISH HARVEST LBS/YR TRM SPORT~ COMMERCIAL"' 294.0 274.9 Nheel er Lake below BFN 1.5xl0 5. 7x10 274.9 259.4 Mi 1 son Lake 5.9xl0 2.2xl9 259.4 - 217.4 Pickwick Lake above YCN 1.3xl0 4.9xl0 217.4 206.7 Pickwick Lake below YCN 3.3x10 5 1.2xl0 5 206.7 161.0 Kentucky Lake (Part 1 of 4) 6.lx10 2.3xl0

                                        ~ !

165.0 121.0 Kentucky Lake (Part 2 of 4) 6.lxl0 2.3x10 121.0 76.0 Kentucky Lake (Part 3 of 4) 1.8xl0 6.8xl0 76.0 22.4 Kentucky Lake (Part 4 of 4) 3.lxl0 l.lxl0

+Oerived from "Situation Assessment    and Planning Assumptions," Oivision of--

Forestry, Fisheries, and Wildlife, TVA, Oecember 1978. ""Oerived from "Estimated Commercial Fish and Mussel Harvest from the Tennessee Valley," Fisheries and Aquatic Ecology Branch, TVA,. 1980.

TABLE 2.4c RECREATION USAGE DATA RIVER SPAN HAHE OF REACH -, HOURS OF USAGE PER YEAR TRM SHORELINE ABOVE-MATER IH-WATER 294.0 274.9 Wheeler Lake below BFH 5.2xl0 6 1.0510 6 4.7xl0 274.9 259.4 Wilson Lake 3.9xl 0 7.4xl0 3.5xl0 259.4 217.4 Pickwick Lake above YCH 2.0xl0 3.5xl0 2.0xl0 217.4 - 206.7 Pickwick Lake below YCN 2.0xl0 6 4.0xl0 5 1.8xl0 6

206.7 165..0 Kentucky Lake (Part 1 of 4) 6.0xl0 1.2x10 5.4x10

                                           ~ 1 165.0  - 121.0 Kentucky Lake (Part   2  of 4)         1.2x10      2.3xl0       l.lx10 121.0  76.0   Kentucky Lake (Part   3  of 4)         2.4xl0      4.7xl0       2.2xl0 76.0    22.4 Kentucky Lake (Part   4  of 4)         2.6xl0      4.9xl0       2.3xl0 t *Based on "Extent of Recreation Observations of Recreation  Use Development and Use of TVA Lake Frontage Property;" (unpublished data from of 1974 Annual Recreation TVA   Reservoirs, Survey); and Division of Reservoir Properties, Recreation Resources Branch,        TVA, 1975.

TABLE 3.I (Sheet I of 4) ENVIRONHENTAL RADIOLOGICAL HONITORING Exposure Path~ay Number of Samples and Sampling and Type and Frequency Locatio Collection Fre uenc AIRBORNE Particulates 5 samples from locations (in Continuous sampler operation Particulate sampler. Analyze different sectors) at or near with sample collection as for gross beta radioactivity the site boundary (LH-I, required by dust lodlng but >24 hrs following filter LH-2, LH-3, LH-4,and LH-6) at least once per 7 days. change. Perform gamna Isotopic C analysis on each sample when 2 samples from control gross beta activity fs locations greater than >IO times the average of control IO mlles from the plant samples. Perform ganma (RH-I and RH-6) isotopic analysis on composite (by location) sample at least once per 92 days. I 3 samples from locations In ccmnunl ties approximately IO miles from the plant (PH-I, PH-2 and PH-3) Radioiodine Same locations as air Continuous sampler operation I-131 every 7 days particul ates with charcoal canister collec-tion at least once per 7 days SOIL Samples from same locations Once every year Ganma scan, Sr-89, Sr-90 once as air particulates per year DIRECT 2 or more doslmeters placed At least once per 92 days Ganma,dose once per 92 days at locations (in different sectors) at or near the site boundary In each of the l6 sector 5

                                                                                  ~ I I

I 4

TABLE 3. I (Sheet 2 of 4) ENV IRONHENTAL RAD IOLOGI CAL HONI TOR ING Exposure Pathway Number of Samples and Sampi lng and Type and Frequency Locatibns Collection Fre uenc 2 or moro dosfmotors placed At least once por 92 days. Gamna dose once per 92 days. at stations located >5 mlles from tho plant In each of the l6 sectors 2 or more dostmeters In at least 8 additional locations of special Interest WATERBORNE Surface I sample upstream (TRH 305.0) Collected by automatic Ganma scan. on 4weok I sample fmnediatety down- sequential-type sampler with compos I te. Compos I to for stream of discharge (TRH 293.5) composite sample taken at tritium at least once por least once per 3I daysa. 92 days Dr Inking I sample at the first potable Col ected by automatic 1 Gross beta and garnna scan on surface water supply down- sequential-typo sampler with 4-week composite. Composite stream from the plant composlto sample taken at for trltlum at least once (TRH 282.6) I sample at loast once por 31 days ~ per 92 days. control location (TRH 305.0) A/VATIC Sediment I sample upstream fran At'oast once por l04 days Ganma scan, Sr-89, and Sr-90 dlschargo point (TRH 297.0) analyses Conyosito samples shall be collected'by collecting an aliquot at inforvals not oxcooding 2 hours, The surface water control sample shall be'onsidered a control.-for tho drinking wator sample. This assenes that the nearest drinking water Intake is >3.0 mlle downstream of the plant discharge. If a drinking water Intake ls constructed within 3.0 miles downstream of the plant 'discharge, sampling I and analysis shall be every 2 wooks.

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TABLE 3. I (Sheet 3 of 4) ENVIRONHENTAL RADIOLOGICAL HONITORING Exposure Pathway Number of Samples and Samp I lng and Type and Frequency Locations Collection Fre uenc of An I sls I sample in Imnediate down- At least once per l84 days Gemm scan, Sr-89 and Sr-90 stree@ area of discharge analyses point (TRH 293.7) INGESTION Hilk At least 3 samples from At least once per 15 days when I-I3I on each sample. Garma dairy farms ln the animals are on pasture; at scen, Sr-89 and Sr-90 at least Iamediate vlclnlty of the least one per 3I days at other once per 3l days plant (Farms B, L and Bn) times. At least I sample from control locations (Farm 0 or C) Fish 3 samples representing At least once per I84 days Ganna scan at least once per comnercial and game species 184 days on edible portions, in Guntersville Reservoir above the plant 3 samples representing carmercial and game species In Wheeler Reservoir near the plant Fruits 8, Vegetables Samples of food crops such At least once per year at Gamna scan on edible as corn, green beans, time of harvest portion tomatoes, and potatoes grown at private gardens and)or farms in the inmedlate vicinity of the plant t "I fs gt

TABLE 3.I (Sheet 4 of 4) ENVIRONHENTAL RADIOLOGICAL HONITORING Exposure Pathway Number of Samples and Sampling and Type and Frequency LocatRons Collection Fre uenc of ARbl sls I sample of each of the same foods grown at greater than IO mlles distance from the plant Vegetation Samples from the nearby Once per 3I days I-I3l, gamna scan once. per (pasturage and dairy farms and 'tlom the 31 days, stations Control samples fram I remote air monitor and I control dairy farm

Table 3.2 Atmospheric and Terrestrial Monitoring Station Locations

             ,I Browns Ferry Nuclear Plant Location and Approximate Distance and Oirection from Plant LM-1 BF                                         .1.0 mile   N LM-2 BF                                          0.9. mile  HHE LM-3 BF                                          1.0 mile   NE LMH BF                                           1.7 miles    HNH LM-6 BF                                          3  miles  SSM PM-1 BF  (Rogersville,  AL)                      13.8 miles    HH PM-2 BF  (Athens, AL)                            10.9 miles    HE PM-3 BF  (Decatur/Trinity,   AL)                 8.2 miles    SSE RM-1 BF  (Muscle Shoals, AL)                     32.0 miles    M RM-6 BF  (Madison, AL area)                      23.0 miles    E Farm 8                                           7.0 miles    HNN Farm Bn                                          4.75 miles    E Farm L                                           5.8 miles    EHE (vegetation only)                        6.1 miles    NE Farm M  (vegetation only)                        6.9 miles    NE Farm C  (control)                                32  miles  N Farm 0  (control)                                26.2 miles    E

TABLE 3.3 Maximum Values for the Lower Limit of Detection (LLD)a c (Sheet 1 of 2) Airborne Food Particulate Fish Products - 'ediment Mater or Gases (pCi/kg, Milk (pCi/kg, (pCi/kg,

 ~Aaai  sis ~Ci/K     ~CI /ma         wet          ~CI /s gross beta     4       0.01          H/A             N/A       N/A           N/A H-3         2000       H/A           H/A             H/A       H/A           H/A Mn-54         15       H/A           130             N/A       N/A           H/A Fe-59         30       H/A           260             N/A ~

N/A H/A Co-58, 60 15 N/A 130 H/A N/A H/A Zn-65 30 N/A 260 N/A N/A H/A Zr-95 30 H/A H/A N/A H/A H/A t Hb-95 I-1 31 Cs-134 Cs-137 Ba-140 15 lb 15 18 60 N/A 0.07 0.05 0.06 H/A N/A N/A 130 150 H/A N/A 15 18 60 N/A 60 60 80 N/A H/A H/A 150 180 H/A La-140 15 H/A H/A 15 H/A H/A

TABLE 3.3 Maximum Values for the Lower Limit of Detection (LLD) ~ (Sheet 2 of 2) Table Notation The LLD is the smallest concentration of radioactive material in a sample-that will be detected with 95 percent probabil1ty with 5 percent probability of falsely concluding that a blank observation represents a "real" signal. For a part1cular measurement system, which may include radiochemical separation: 4.66 s LLD 2.22 Y exp(-Xht) E V Where: LLD 1s the "a prior1" lower 11mit of detection as defined above, (as p1cocuries per unit mass or volume).- sb is the standard deviation of the background counting rate or of the counti'ng rate of a bla'nk sample as appropriate, (as counts per minute). E is the counting efficiency, (as counts per disintegration). V 1s the sample s1ze (in units of mass or volume). 2.22 is the number of dis1ntegrat1ons per minute per picocurie. Y 1s the fract1onal rad1ochem1cal y1eld, (when applicable). 1s the r'adioactive decay constant for the particular radionuclide, and for environmental samples is the elapsed time between sample collection, (or end of the sample collect1on period), and time of counting (for environmental samples, not plant effluent samples). Typical values of E, V, Y, and ht should be used in the calculation. It should be recognized that the LLg is defined as an ~a riori (before the,. .= system and not as' fact) limit

                                       )lii t representing the capability of a measurement f

LLD for analysis of drinking water and surface water samples shall be performed by gamma spectroscopy at approximately 15 pCi/a. If levels greater than 15 pCi/K are identified 1n surface water samples fownstream from the plant, or in the event of an unanticipated release of I-l3l, drinking water samples will be analyzed at an LLD of 1.0 pCi/K for I-131. Other peaks which are measurable and 1dentifiable shall be identified and reported.

Figure Land SXCe l.l Boundaz'y

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Elevateg I Release (600') from common stack RH 90-147 A&B FI90-221 Dilution (1 of 3) SJAE Prom SGTS Steam Packing Exhauster (common) Hech. Vacuum Pump Condenser 4 Recomblners A& i 8000 cuft lloldup Volume I ,Charcoal Adsorber Vessels Pigure 1. 2 f BPN Of gas System and SC1'S Effluent Honitoring I l

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                   *Roof Fans Refuel Floor RH 90-249                       RH 90-251                                          RH 90-250 Turbine Deck From Primary Containment, Purge System From Radwaare
                                                                                                           ~ Building Turbine Building (Typical for each unit)                                                 Rea'ctor Building Control            (Typical for each 'unit)   to SGTS Bay                                   (emergency  ventilation)

Roof Fans used seasonally to control temperature Figure la3 BFN .Normal Building Venti.lation I,

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(SIieet 1'of 4) 1.0 0.9 0.8 D 0.7 U Z Z 0.6 UJ 0.5 Z 0 o 0.4 0.3 0.2 0.1 I 0.1 1.0 10.0 100.0 200.0 PLUME TRAVEL DISTANCE (KILOMETERS) ., I I ~ j~ I Plume Depletion Effect for Ground Level Releases (All Atmospheric ~ ~ Stability Classes) ~ tt vi>

(Sheet 2 of 4) 1.0 STABLE 0.9 NEU TR AL (E,F,G) ~u 0.6 D CL pp (3 UNSTABLE z 06 (A,B,C) g 0.5 z 0 0.4 ts: 0.3 0.2 0.1 0.1 1.0 10.0 100.0 '00.0 PLUME TRAVEL DISTANCE (KILOMETERS) Plume Depletion Effect for 30m Releases (Letters denote Pasquil( Stability Class) ~ ~ S

                                        ~
                                                                      '  p  ~

Piguxe 1,4 ($ heet 3 qf 4) 1.0 STABLE (E,F,G) 0.9 N EUTRAL w 08 (D) Z D 0.7 UNSTABLE U (A,B,C) z 0.6 w p6 z 0 I- p4 K

 '.3 0.2 0.1 0.1 1.0                                    10.0                 100.0      200.0 l

PLUME TRAVEL DISTANCE (KILOMETERS) 1 Plume Depletion Effect for 60m Releases (Letters denote Pasquill Stability Class)

Fi 1,4 (Sheet 4 of 4). 1.0 NEUTRAL (D) 0.9 uj 0.8 D UNSTABLE (A,B,C) 0.7 U STABLE (E,F,G) .z NO DEPLETION 'z 0.8 (FRACTION REMAINING 0.5 Z 0 o~ 0.4 IX 0.3 0.2 0.1 0.1 1.0 10.0 100.0 200.0 I PLUME TRAVEL DISTANCE (KILOMETERS) I I Plume Depletion Effect for 100m Releases (Letters denote Pasquill Stability Class) b

~ ~

k

Figure 1.5 , 100 I I I D 10 0.1 1.0 10 PLUME TRAVEL DlSTANCE (KILOMETERS) Figure 1. Vertical Standard Deviation of Material in a Plurne (Letters denote Pasquill Stability Class)

Figure 1,6. (.Sheet 1 qf 4) 10 3

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104 LX I I I I I i I I I s I I I CC l- . tX 10< I-Q

l-CC 10-,7 0.1 1.0 10.0 100.0 200.0 PLUME TRAVEL DISTANCE (KILOMETERS} Relative Deposition for Ground Level Releases (All Atmospheric Stability Classes}

I Fi:gure 1,6. ($ heet 2 or 4) 10 3 UNSTABLE (A,B,C) I I I I I ~ t I I I I I I CC NEUTRAL I-l I Z NEUTRAL (D) 10~ I I l I STABLE I I s r O UJ 0 I-LLI tX ST BLE (E,F, G) 10 10 7 0.1 1.0 10.0 100.0 200.0 PLUME TRAVEL DISTANCE (KILOMETERS) Relative Deposition for 30m Releases (Letters denote Pasquill Stability Class)

Figure 1.6 (Sheet 3 of 4) UNSTABLE (A.B ,C 10-6 NEUTRAL (D) K UNSTABLE LU I- NEUTRAL tt: 10-6 I- 1 I I CO I I 0 Q )I-LLI LLI 10 7 STAB LE (E,F,G) 10-8 0.1 1.0 100.0 200.0 10.0'LUME TRAVEL DISTANCE (KILOMETERS) Relative Deposition '.or 60m Releases (Letters denote Pasquill Stability Class)

Figure 1.6 (Sheer. 4 of 4) UNSUB L E (A,B C)

I I NEUTRAL (D) BLE (E,F,G) NQ DEPLET lQN 1.0 10.0 100.0 200.0 PLUME TRAVEL DlSTANCE (KlLOMETERS) Relative Deposition for 100m Releases (I etters denote Pasquill Stability. Class)

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CONDENSER COOLING MATER INTAKE BAY RllR SERVICE WATER

TURBINE LOOP .1 RH 90133 BUILDING RllR I.OOP 2 (3) Rll R RH 90134 (2) Rx BUILDING RAtl TENNESSEE COOLING RIVER RADWASTE MATER (CON lON) RH 90130 OPENING FOR llEI,PER kf)D ' DIFFUSER (1) TURBINE BUILDING EQUIPMENT (2) REACTOR BUILDING EQUIPHENT (3) CONDENSER 'LIWDOWN FgON COOLING TOWI'.RS

                                                                  'l'0 COOI.l NG
                                                                    'i'OMERS Figure 2.2 . Bl'H LT(fUTD EFFl.Ul':NT HONITORS       ('I'yp'Ical. Uui L'  Con)i))ou Ita(lweste)

4 FI.OOR F1 77-60 FLOOR 1'I.OOR DRAIN FI.OOR DRAIN DRAIN SAHPLE DRAINS COLLECTOR 1"II.TER TANKS TANK RH 90-130 I.AUNDRY DRAIN TANKS EOUIPHENT DRAINS WASTE WASTE WASTE WASTE CONDENSATE COLLECTOR FILTER DEHINERALIZPR SAHPI,E STORAGE TANK TANKS TANKS Figure 2.3 )- Liquid Radvaste Treatment System

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Figure 3.'1 ATMOSPHERIC AND TERRESTRIAL MONITORlNG NETV/ORK'LAWR" NCE BURG gPUCMKI FAY r r cVIt L WILSONc WHE Lc R OAM " ROG E SVILr O ..I FLORENCc. <<THENS SHEFFI~ MUSCL= SHOALS BP.OWNS FE. RY HUNTSVILLE iU rcAR PL NT Lc GHr ON TUSCUMBIA H COURT'N~f OEC<<l UR IO MILES gRUSSEr LVILLE GUNT RSVILL e HARTSEr LE OAM 25 MILES HAI cYVII LE yCULLMAN 45 iMII ES 0-ENVIRONMENTAL MONITORING STATION

Figure 3. 2 LOCAL MONITORING STATIONS BROGANS FERRY NUCLLAR PLANT ATHENS U.S. HWY 72 p C 0 EFi'lP lr JP ALA. HWY 20 Legend

 '0   Air Monitor                                           DECATUR Oairy Farm Q   Other Farm Scale O     I     2     3    4    5 Miles

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R ES ER VOI R MONITOR IN 6 NETVlOR K Etk River V/Hi:"LER DAM mile. 27450 Rogersvitte 0 mile 282.6 Athens Q mile 285.2

                                                       =..". NUCLiW PLANT jO Champion mile 257.0 Paper   Co.

mite 293.50 mile 305.0 Cour tfand mile 29370 Decatur Scale of Miles

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ML18032A530

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