ML18033A661

Semiannual Radioactive Effluent Release Rept Browns Ferry Nuclear Plant,Changes to Odcm.

ML18033A661
Person / Time
Site:	Browns Ferry
Issue date:	07/20/1988
From:	TENNESSEE VALLEY AUTHORITY
To:
Shared Package
ML18033A659	List: ML18033A658 ML18033A660 ML18033A661 ML18033A662
References
PROC-880720-01, NUDOCS 8903100158
Download: ML18033A661 (55)

Text

ENCLOSURE 3 TENNESSEE VALLEY AUTHORITY SEMIANNUAL RADIOACTIVE EFFLUENT RELEASE REPORT BROGANS FERRY NUCLEAR PLANT CHANGES TO THE BFN OFFSITE DOSE CALCULATION MANUAL S903100158 S90302 PDR ADOCK 05000259 R PDC ver r ~ r r e r r rg gvr r r rr v v' r r t ~

Handling of Changes ta the BFN Offsite Dose RARC OP 9 Calculation Hanual Revision 0 Page 4 of.4 Appendix 1 BFN OOCH Change Description Form D

a. l 't Description of change:

o~ 1 V rn z.

z.

l 5

CJQ 5 Pages affected: ~ P o-3usti fication. for change:

~pi Srd a s

~I Analysis of'ffect of change'on dose calculations, projections, or'etpoint calculations:

~ M rv1o~z a.t.g Attach marked-up pages from the c rr revision of the SQN OOCH which show the change.

RARC Review; Date:

RARC Chairman I 0628o/COC4

~ 1 ~ 8 ~ Iiei 4

~ %JleA 1M I1

Handling of Changes to the BFH Offsite Dose AARC QP 9 Ca l cu1a t i on Hanua1 Revision 0 Page 4 of 4 Appendix 1 8FH ODCH Change Description Form Description of change:

Pages affected: MS% 0 P Aa.ve an I

)

Jus t i fi ca t ion for change: < UM Analys/s of effect of change on dose calculations, projections, or setpoint calculations:

c cc t Attach marked-up pages from the cur e'n~trevision of the the change.

AAAC Aevie~:

AAAC Chairman SQN QQCH which sho~

Date: >a F 0678o/COC4

/

QN Handling of Changes to the 8FH Offsi te Dose RARC OP 9 Calculation Manual Revision 0 Page 4 of 4 Appendix l 8FH ODCM Change Description Form Oescription of change; vo C

4c}c. l 0 Pages affected:

Just)fication for change: . sc ao 'in ghi,,

Analysis of effect of change on dose calculations, projections, or setpoint ca) cul ations:

llli5 l ~,k Attach marked-up pages from the current revis1on of the SQN OOCM wh1ch show the change.

RARC Review:

RARC Chairman Date l~ Q 0678o/COC4

Handling of Changes to the BFN Offsite Oose RARC OP 9 Calculatio~ Manual Revision 0 hne g v5 Page 4 or 4 Appendix I BFN QQCa1 Change Description Form oeecrtntton of change: / Ge o ' rr g1 je <k. W/pr6p 5~/(~ 'nrem ' I j~ / A I'MC'. +~+V/ C

~Pti 4 toe

~o~d e~~r <a 4 S ~ /i~g rr u re m~f '

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Pages affected: ( i F >+s~r7 (g /Zg(to g, P H t d 6 4nHi) .

3ustification for change: t /'s~/e e

'Y<AP~d~m Md-r ae'Vt I C At/Or j ~le s( p er Ire V

e dm @Mr gdmrC ~ . /7e> <re 0 e pl t'.d p 7 AORS Cp tne O7 i'oe st P q ipoYc(~ w D8'8 vlU ~ g(Pdf y/1 Analysis of effect of change on dose calculations, projections, or setpoint calculations:

J Cr/ g~tc>> Vt Or / Veet dog cw(c.~ l~ io/ s ro t ac.Yi>v > go~ 5+~ o/'~H 9/3e/g'5 CkAC rtttriM Attach marked-up pages from the the change, cvvr~~~n-of the Sqw OpCH which show RARC Review:

RARC Chairman Date: 6 /

0678o/COC4 TVA 7Ã9C (Oheee [ 4y)

I

~

RETS Manual Revision 4 Page 39 LIST OF FIGURES Fi e Number Title BFN - Land Site Boundary 1'. 2 BFN Offgas System and SGTS Effluent Monitor ng 1.3 BFN Normal Building Ventilation 1.4 (Sheets 1-4) Plume Depletion Effect (All Atmospheric Stability Classes) 1.5 Vertical Standard Deviation of Material in a Plume (All Atmospheric Stability Classes) 1.6 (Sheets 1-4) Re'at've Deposition (All Atmospheric Sta'oi'ty Classes) 4 2.1 Assumed Liquid Effluenb Restricted Area 2 2 BFN Liquid Effluent Monitors

~ ~

~ 2oQ ~ ~ Liquid Radwaste'reatment System

~, ' ~ ~

3.1 '.'nvironmental Radiological Sampling Locations within 1 mile of plant 3.2 Environmental Radiological Samo ling Locat'ons From 1 to 5 miles from the plant 3.3 Environmental Radiological Sampling Locations Greater than 5 miles from the plant 1976p

lj MQ~'

RETS Manual Revision 4 Page 40 1.0 Gaseous Effluents 1.1 Alarm/Trio Set pints Specification 3.8.B.L requires that the dose rate at or beyond the site boundary (Figure 1.1) due to gaseous effluents from the site shaJ.L be limited at all times to the following values:

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

2. 1,500 mrem/y to any organ from radioiodines and particul.ates.

Specification 3.2.K.L requires gaseous eff uent monitors to have alarm/trip setpoints to ensure that the above dose rates are not exceeded. This section of the ODCM describes the methodology that will be used to determine these setpoints. Figures 1.2 and 1.3 show the Offgas System, the Standby Gas Treatment System and normaL building ventilation with effluent monitor locations.

The methodology Eor determining alarm/trip setpoints is divided into two major pa ts. The fi st consists of backcalculat'ng from a dose rate to a re'ease rate limit, in pCi/s, for each nuclide and release point.

The secorid consists of using the release rate limits to determine the physical settings on the monitors. The methodology for the latter is contained in

. ~ 'r',I

~ ~

Technical instruction 15.

1.1.1

~ ~ f ~ I

~ ~

~ ~

Release Rate Limit Methodolo .Dose Rates First, a dose rate is calculated based on the design objective source te m mix used in the li'censing of the plant. Dose rates are determined for (1) noble gases and (2) iodines and particulates.

Release Rate Limit Methodolo Dose Rates Noble Gas Dose rates are caLculated for total body and sk'n, due to submersion within a cloud oE noble gases, using a semi-infinite cloud model. The use of a finite cloud modeL would result in calculated doses of 0 to 10 pere nt higher than those calculations using the semi-infinite cloud model Eor BPH. The dose rates are evaluated at the offsite locations with the highest expected concentrations, i.e., the nearest land site boundary points in each sector (from Table 1.1) and at other locations expected to be the maximum exposure points.

The nobl.e gas radionuclide mix used in this calculation is based on the design objective source term given in Table 1.2. Dispersion oE the released radioactivity is handled as described in Section 1.7 using historical. annual average meteorological data given in Table 1.3.

No credit is taken for shielding by residence.

1976p

RETS Manual Revision 4 Page 41 To calculate the dose rate from radiological effluents discharged from a given release point for any one of the potential maximum-exposure points',

the foll'owing equations are used..

Total Bod Dose Rate Xi DFBi (1.1) where DTB = total body dose rate, mrem/y.

Xi ~ air concentration of radionuclide i, pCi/ms. Air concentrations are calculated as described by Equation 1.14.

DFBi '. ~ total body dose factor due to gamma radiat'on, mrem/y per pCi/m~ (Table 1.4).

Sk'n Dose Rate Ds ~ $ Xi (DFSi + 1.11 DFYi) (1. 2)

~

whe.re . ~

~

~

~

t .~ o ~ ~ ~ )

Ds skin dose ra"e','. mrem/y, S

Xj:' air concentration of radionuclide i, pCi/m . Air concentrations are calculated as described by Equation 1.14.

DFSi skin dose factor due to beta radiation, mrem/y per pCi/m ~ (Tab le 1. 4) .

the average rat.o of tissue to air energy absorption coefficients, mrem/mrad.

DFYi gamma-to-air dose factor for radionuclide i, mrad/y per pCi/ms (Table 1.4).

The total body and skin dose rate calculations are repeated for each release point. Dose rates for releases from all building vents are summed. The maximum stack and building vent total body and skin dose rates will be used to determine release rate limits.

1976p

RETS manual Revision 4 Page 42 Release Rate Limit i4fethodolo Eodine and Particulate Dose Rates For setpoints, the iodine and particulate dose rates are. calculated for the design objective source tezm given in Table 1.2. Dose rates are calculated for the critical organ, thyroid, of the critical age group, infant. Pathways considered are inhalation, ground contamination and milk ingestion. The dose rates are evaluated at the offsite locations with the highest expected concentrations, i.e., the nearest land site boundary points in each of the'16 sectors (from Table 1.1) and at other locations expected to be the maximum exposure points. This calculation assumes that a (hypothetical) cow is at each of these locations. These cows are assumed, conservatively, to obtain 100 percent of their food from pasture grass.

The inhalation, ground contamination, and milk ingestion dose rates (in mrem/year) for the selected organ (thyroid) and age group (infant) are calculated using Equation 1.13 as described in section 1..5.3. For determining the total thyroid dose rate from iodines and particulates:

DTa = Der + DTaG + D~ (1..3) where:

= total thyroid dose rate, mrem/yr.

Mz ~ thyroid dose rate due to inhalation, mrem/yr.

'DTBG ~ total body dose rate due to ground contamina"don,'rem/yr:.

The"thyroid dose rate is assumed to be equal to the total

~

body dose rate for this pathway.

~ ~

0

= thyroid dose rate due to pasture grass-cow-milk ingestion, mr em/yr..

The above dose rate calculation is repeated for each release point. Dose rates for releases from all building vents are summed. The maximum stack and building vent thyroid dose rates vill be used to determine release rate limits.

3 1976p

p.

'L,. (Qp RETS Manual Revision 4 Page 43 Release Rate Limit Methodolo - Setooints The dose rate limits of interest (Specification 3.8.B.1) are:

Total Body ~ 500 mrem/yr Skin ~ 3000 mrem/yr Maxiarum Organ ~ 1500 mrem/yr These limits are d'vided by the corresponding calculated dose rates (fzom Equations 1.1, 1.2, and 1.3):

Total Body Dose Rate Limit RTB(vent oz stack)

(vent or stack)

Skin Dose Rate Limit RS(vent or stack)

DS (vent or stack)

Maximum Organ Dose Rate Limit R~(vent or stack)

DTH (vent or stack) 0 .

~

These ratios represent how far above or below the dose zate calculations were.

~ ~ ~ ~

A.'hota1.release rate,

~ ~

~ ~

guidelines the

~

p Q, for each nuclide .type (noble gas or

~ ~ ~

~

'i;odine/particulate) and release point (building v'ent or stack) is calculated, using the source term data in Table 1.2. Thus, four total release rates are calculated:

= Total noble gas release zate f om building exhaust vents, Ci/s.

= Total noble gas release rate from main stack, Ci/s.

Qipv = Total iodine and particulate release rate from building exhaust vents, Ci/s.

Qips ~ Total iodine and particulate release rate from main stack, Ci/s.

To obtain a release rate limit, r, foz each nuclide type and release point, the total release rate, Q, for that nuclide type and release point is multiplied by the corresponding ratio, R:

1976p

RETS Manual Revision 4 Page 44 For noble gases released from building vents:

rngv'TBv Qngv~ or

~ RSv Qngv whichever is more restrictive, i.e., smaller.

where rngv = Calculated release rate limit for noble gases released from building vents.

RTBv ~ Ratio of total body dose rate limit to totalbody dose rate for building vent releases, as calculated above.

~ Total Table 1.2 noble gas release rate from building vents.

RSv = Rat'o of skin dose rate limit to sk.'n dose rate for building vent re'eases, as calculated above.

For noble gases released from the stack:

rags RTBs Qngs> ~ ~ ~ ~

.>Ss Qngs

~y ~ ~

~ ~ ~

wh'chever is more'restrictive, i.e.,

smaller'here rngs = Calculated release rate limit for noble gases released from the stack.

RTBs ~ Ratio of total body dose rate limit to total body dose rate for stack releases, as calculated above.

Qngs = Total Table 1.2 noble gas release rate from stack.

RSs ~ Ratio of skin dose rate limit to skin dose rate for stack releases, as calculated above.

1976p

RETS Nanual Revision 4 Page 45 For iodines and particulates with half-lives greater than 8 days released from building vents:

ripv RTHv Aipv where ripv ~ Calculated release rate limit for iodines and particulates released from building vents.

= Ratio of maximum organ dose rate limit to maximum organ dose rate for building vent releases, as calculated above.

Qipv ~ Total Table 1.2 iodine and particulate release rate from building vents.

For iodines and particulates with half-lives greate .than 8 days released from the stack:

rips = RTHs blips where rips ~ Calculated release rate I&it'or iodines and.particulates released Crom 'the stack.

~

d ~ ~ ~ ~

~ ~ ~~

~

RTHs =.Ratio of maximum organ dose rate limit to maximum organ ..

dose rate for stack releases, as calculated above.

Qips = Total Table 1.2 iodine and particulate release rate from stack.

The release rate limits, r, calculated for BFN using this methodoLogy are:

Noble Gas Iodine and Particulate Stack rags 1.4 E+01 Ci/ rips 3 ~ 57E&5 Ci/s Building Vents rngv ~ 1.50E-OL Ci/s ripv ~ 2 '9E&6 Ci/s The values listed are used as administrative guidelines for operation and for development of alarm/trip setpoints (see Technical 1976p

RETS Manual Revision 4

)&JAN'nstruction Page 46

15) to ensure that instantaneous dose rates do not.

exceed release rate limits.

Instantaneous release rates, q in Ci/s, for each nuclide type and release point are limited by the following equations:

For noble gases, Catv + 'lings c i

0. 15 14. 4 For iodines and particulates, qipv +

qips c 1 2 19E-06 3.57E-05 where

= instantaneous noble gas release rate from bu:1ding vents, Ci/s.

qngs = instantaneous noble gas release rate from the stack, Ci/s.

qipv ~ instantaneous iodine and particulate release rate from building vents, Ci/s.. .o< ~

~ ~

~ ~

'i'ps

~ ~

~. ins'tadtarfeous iodine and particulate releas'e rate from 'the

'.stack, Ci/s. ~ y

~ ~

1.2 Nonthl Dose Calculations Dose calculations will be performed once per 31 days to determine compliance with specifications 3.8.B.3 and 3.8.B.5. These specifications require that the dose at or beyond the site boundary due to gaseous effluents from each reactor at the site shall be limited to the following:

For noble gases,

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

2. During any calendar year, 10 mrad to ai'r for gamma radiation and 20 mrad to air for beta radiation.

1976p

RETS Manual Revision 4 Page 47 For I-131, I-133, Tritium and particulates with half lives greater than 8 days,

1. During any calendar quarter, 7.5 mrem to any organ.

2. During any calendar year, 15 mrem to any organ.

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

Doses will be calculated us'ng the conservative model described~in Sec"ions 1.2.1 and 1.2.2. If the monthly fract'on of the annual one-unit Technical Spec" ficat'on Limit is exc eded, a realistic model, described in Sections 1.2.3 and 1.2.4, will be used.

1.2.1 Yonthlv Noble Gas Dose (Conservative Yodel)

Doses to be calculated are gamma and beta ai" doses due to exposure to a semi-'nfinite cloud of noble gases. The use of a f" nite cloud model would result :n calculated doses oi 0 to 10 percent h ghe" than those calculations us.'ng the semi-infinite c'oud model for BRf. Releases of Ar-41, Kr-85m, Kr-85, Kr-87, Kr-88, Xe-131m, Xe-133m, Ze-133, Xe-135m, Xe-135, and Xe-138 are conside ed.

Because only these nuclides are considered, the dose is divided by 0.9, to account for a possible 10 percent contribution of. dose from o ther'uclidep.

r

~ ~

~ ~

The dispe"sion facto). used wilt be the highest annual-average g/Q based on 1977-1979 'meteorological data (Table 1.3). Dispersion.

factors are calculated using the methodology described by Equation 1.15. Stack releases are considered elevated releases.

~

All other vent releases will be treated as ground level.

No cred't is taken for radicactive decay.

Monthly Conservative Model - Gamma dose to air (X/Q)

Dg 0.9 3.15x10 7

~ i Yi (1.4) where:

~ gamma dose to air, mrad.

X/Q ~ highest land-site boundary annual-average relative concentration, s/m3 (from Table 1.1}.

~ 1.84x10 6 for ground level releases,

~ 2.08x10 8 for elevated releases (stack).

1976p

RETS Manual Revision 4 Page 48 0.9 ~ fraction of total gamma dose expected to be contributed by the assumed nuclides.

10~ pCi/Ci conversion factor.

3.15xl0 ~ ~ slyr conversion factor.

~ monthly release of radionuclide i, Ci.

DFYi ~ gamma-to-air dose factor for radionuclide i, mrad/yr per pCi/ms (Table 1.4). For Kr-88 and Xe-138, the dose for Kr-88+D and Xe<<138+D are- used to account 'actors for daughter buildun.

Monthl Conservative Model - Beta dose to air (X/Q) los (1.5) 0.9 3.15xl0 7 whe e:

~ beta dose to air, mrad.

X/Q ~ highest land-site .boundary annual-average relative concentration, s/ms (from Table 1.1). ' '

0

~ 1.84x10 6 'For gr'ound level'eleases~

'r ~

g ~ 2.08x10 .8 for elevated releases (stack). ~ : ". ~ . ~

~r ~~ ~ ~ ~ ~ ~~

~ fraction of total beta dose expected to be contributed by the assumed nuclides.

pCi/Ci conversion factor.

3. 15xlo 7 s/yr conversion factor.

Qi monthly release of radionuclide i, Ci.

DFQi beta-to-air dose factor for radionuclide i, mrad/yr per pCi/m~ (Table 1.4). For Kr-88 and Xe-138, the dose factors for Kr-88+D and Xe-138+D are used to account for daughter buildup.

1976p

0' C .

RETS Manual Revision 4 Page 49 1.2.2 Monthl dose from Eodines Particulates and Tritium (Conservative Model)

Doses are.to be calculated for the infant thyroid from milk ingestion and for the child bone and teen gastrointestinal tract (GIT) from vegetable ingestion. Releases of H-3, I-131, and I-133 are considered for the milk path~ay. 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 GIT. The most critical real cow location is considered for the milk pathway and the most critical location w"'th a home-use garden is considered for the vegetable pathways (see Table 1.1). The cow is assumed to graze on pasture grass for the whole year.

The highest annual-average X/Q and D/Q based on 1977-1979 meteorological data (Table 1.3) will be used for ingestion pathway locations. Dispersion values are calculated .as described by Equations 1.15 and 1.16. Stack releases are consi.dered elevated releases. All other vent releases will be treated as ground level.

No credit is taken for radioactive decay.

Doses a" div.'ded by 0.9 to account for a possible 10'percent contribut'on from othe" nuclides.

Monthl Conservative Madel' Enfant Th roid Dose from Milk In estion The monthly'thyroid dose from.pulk'ngestion is calculated using, the following

-'quation .i

~ ~

~

~0 ~ ~ ~

PQi:.RCPi) D/Q 10 + (QT RCPT) X/Q DTH (1.6) 0.9 x 3.15xl0 ~

'here Qi = monthly release of iodine nuclide i, Ci.

QT ~ monthly release of H-3, Ci.

RCpi = E-131 or E-133 pasture grass-cow-milk ingestion dose factor for infant thyroid, mrem/yr pe pCi/mz-s. Dose factors are calculated as described in Section 1.6.1.

~ H-3 pasture grass-cow-milk ingestion dose factor for infant thyroid, mrem/yr per pCi/cc. The dose factor is calculated as described in Section 1.6.7.

>> lo-1976p

RETS Manual Revision 4 Page 50 D/Q highest relative deposition rate for a location with an identified milk cow, m"~ (from Table 1.1).

3.16x10 10 for ground level releases, 2.30x10 1 for elevated releases (stack) ~

X/Q highest relative.air concentration for a location with an identified milk cow, s/m~ (from Table 1.1).

1.47xl0 07 for ground level releases, L:69x10 08 for elevated releases (stack).

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

3.15xl0 ~ s/yr.

10~ pCi/Ci.

Monthly'Conse ~ative Model - Child Bone Dose from Ve etable In est.'on The monthly bone dose from vegetable ingestion is calculated using the following eq~~t.'on:

E (Qi DFi) D/Q 10 + QT DFT X/Q 0 where DBC 0.9 x 3.15xLO~

~ 4 i monthly release'of

~

~ 'I ~

4.

~

tg ~

~

~

~

~

~

Qi "

~ ~

. Sr or CS duclide i, Ci.

= monthly release of H-3, Ci.

DFi = Total vegetable ingestion dose factor to child bone for Sr-89, Sr-90, Cs-134 or Cs-137, mrem/yr per pCi/m~-s.

~ RVFi + RVSi, where RVFi is the dose factor for fresh leafy vegetables (as calculated in Section 1.6.5) and RVSi is the dose factor for stored vegetables (as calculated in Section 1.6.6).

DFT ~ Total vegetable ingestion dose factor for child bone for H-3, mrem/yr per }tCi/cc.

~ RVFT + RVST, where RVFT is the tritium dose factor for fresh leafy vegetables (as calculated in Section 1.6.11) and RVSi is the tritium dose factor for stored vegetables (as calculated in Section 1.6.12).

1976p

RETS Manual Revision 4 Page 51 D/Q ~ highest relative deposition rate for a location with an identified home use garden, m ~ (from Table 1.1).

~ 4.46xL0~9 for gzound level releases,

~ 1.13xLO 09 for elevated releases (stac'k).

X/Q ~ highest relative air concentration for a location with an identified home use garden, s/m3 (from Table 1.1).

~ 1.57xLO 06 for ground level releases,

~ 9.50xLO 09 for eLevated. releases (stack).

3.15xL07 = s/yr.

~ pCi/Ci.

0.9 ~ fract.'on of total child bone dose expected to be contributed by H-3, Sr-89, Sr-90, Cs-134, and Cs-137.

Nonthl Conservative Model Teen Gastrointestinal Tract (GIT) Dose Ezom Ve etable In est'on The month y t en GIT dose f"om vegetable ingestion is calculated using the following equa 'on:

0-

~

~ ~

~

where t

'I ~

~~

(Q DF')'D/Q

0. 9 m.

~ ~

1

~

10

3. LSxLO >

+ QT DFT C

X/Q u.s) 4~

Qi monthly release of cobalt nuclide ig. Ci.

monthly release of H-3, Ci.

DFi Total vegetable ingestion dose factor to the teen GIT foz Co-58 or Co-60, mzem/yr per pCi/m~-s.

RVFi + RVSi, whe e RVFi is the dose factor for fresh leafy vegetables (as calculated in Section 1.6.5) and RVSi is the dose factor for stored vegetables (as calculated in Section 1.6.6).

DFT = Total vegetable ingestion dose factor to the teen GIT for H-3, mrem/yr per pCi/cc.

~ RVFT + RVST, where RVFT is the tritium dose factor for fresh leafy vegetables (as calculated in Section 1.6.11) and RVST is the tritium dose factor for stored vegetables (as calculated in Section 1.6.12).

-12>>

1976p

RETS Manual Revision 4 Page 52 D/Q ~ highest relative deposition rate for a location with an t identified home use garden, m ~ (from Table 1.1).

= 4.46x10 09 for ground leve'1 releases,

~ 1.13x10 09 for elevated releases (stack).

X/Q ~ highest relative air concentration for a location with an identified home use garden, s/ms (from Table 1.1).

~ 1.57xl0 06 for ground level releases, 9.50x10 09 for elevated releases (stack).

3.15xl0 ~ = s/yr.

~ @CD/Ci.

0.9 ~ fraction of total teen GIT dose expected to be contributed by H-3, Co-58, and Co-60.

Total Monthl Dose Comoar'son to Limits The calculat d g~~a-air and beta-a'r doses are compared to tNe monthly fract'on of'he annual one-an.'imit for these doses, '.e., 0.83 mrem

.for gamma-air and 1.67 mrem 'or beta-air. The maximum monthly organ dose is the highest of the three doses calculated; it is compared to the monthly fraction of its annual limit, i.e., 1.25 mrem. If any of the doses calculated by the conservative monthly dose model exceed the

~ .

~ ~

monthly fraction of the one-unit annual Technical Specification limits, a more comprehensive dose assessment will be performed as descr'ibed 'below..

For doses Calculated to be less than these gimits, the res'ults"of the

.~ conservative monthly model will be used .to determine cumulative'uarterly anB annual doses as described in Section 1.2.5.

1.2.3 Monthl 'Noble Gas Dose (Realist.'c Model)

In the realistic model, all measured rad'onuclides are used to calculate garrma and beta ai" doses. ~ The dose is evaluated at the nearest land site boundary point in each sector and at other locations expected to be maximum. exposure points using a semi-infinite cloud model. 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 BFN.

Historical onsite meteorological data from the period 1977-1979 (Table 1.3) will be used to calculate dispersion factors as described in section 1.7. Stack releases will be considered elevated releases.

Radwaste and reactor building releases will be considered split-level releases. Turbine building releases will be treated as ground level.

Radioactive decay is considered in this calculation.

The monthly release is averaged over one year to obtain an average release rate.

- 13 1976p

RETS Manual Revision 4 Page 53 Realistic Model - Gamma dose to air D~n = tm 7 Xni DFyi (1.9) vhere:

Dyn ~ gamma dose to air for sector n, mrad.

Xni ~ air concentration of radionuclide i in sector n, pCi/m~. Air concentrations are calculated as desc"ibed'y Equation 1.14.

"-gamma-to-air dose factor for radionuclide i, mrad/yr per Dpi pCi/m3 (Table 1.4).

~ time. period over which the release is averaged, yr.

Realist.'c Model Beta dose to air

'n = m 7 Xni Bi (1. 1.0) vhere:

DBn

~ ~ ~

beta dose to air for sector n, mrad;

. 'Kn'i '

~ ai'r concentration hf radionuclHe. i in'sector n,

' pCi/m3. Air concentrations aie dalculated as described by Equation 1.14.

Dpi "-beta to air dose factor for radionuclide i, mrad/yr pe'r pCi/m~ (Table 1.4).

= time period over which the release is averag d, yr.

The highest gamma-air and beta-air doses calculated will be used in the cumulative quarterly and annual dose determination to check compliance vith Specification 3.8.B.3.

1.2.4 Iodines Particulates and Tritium (Realistic Model)

Doses for releases of iodines, particulates, and tritium will be calculated using Equation 1.13 given in Section 1.5.3. The calculation vill consider all measured radionuclide releases. The dose will be evaluated for all organs and all age groups, and the maximum organ dose selected. Actual land use survey data and grazing information vill be used to determine the dose for real individuals and pathways.

- 14 1976p

(',)

RETS Manual Revision 4 Page 54 Historical onsite meteorological data from the period- 1977-1979 (Table 1>>3) will be used to calculate dispersion factors as described in section 1.7. Stack releases will be considered elevated releases.

Radwaste and reactor building releases will be considered split-level releases. Turbine building releases will be treated as ground level.

The highest organ dose for a zeal receptor is determined by summing the dose contribution from all real pathways including ground contamination, inhalation, vegetable ingestion (for identified garden locations), cow and/or goat milk ingestion (if a cow or goat is identified for the location), be f ingest'on (the beef ingestion dose for the location of highest beef dose for all rec ptozs wi11 be considered the beef dose for all zeceptors). The receptor having the highest ozgan dose is then used in the cumulat've quarte ly and annual dose determination to check complianc with Specification 3.8.B.5.

1.2.5 Cumulatve Ouarterl and Annual Doses Cumulative calendar quarte doses are est'mated by su~ing the doses calculated foz each month in that quart . Cumulative calendar year doses aze estimated by su~ning the doses calculated for each month in that yeai. The cumulative calendar quarter and calendar year doses are compared to their respective one-unit Technical Specification limits to determine compliance; If any limit is exceeded, a determination will be made to apportion the dose between the reactor units in accordance with the releases .that can be assigned to each.

~ >> ~ ~.>> ~

>> . ~~ ~ ~ ~~ ~ ~ ~

~ ~ '>> ~

1976p

RETS ManuaL Revision 4 Page 55 1.3 uarterl. Dose Calculations A complete dose analysis utilizing the total estimated gaseous releases for each calendar quarter vill be performed and reported. as required in Specifications 6.7.5. Methodology for this analysis is that which is described in Section 1.5, using the quarterly release values reported by the plant personnel. All real pathways and receptor locations (as identified in Table 1.1) are considered. In addition, actual meteorological data representative of each corresponding calendar quarter w.'ll be used to calculate disoersion factors as descri'bed in section 1.7. Stack z'eleases will be conside ed el.evated releases.

Radwaste and r actor building releases vill be-considered spl.it-level r leases. Turbine bu'lding releases will be treated as ground level.

The highest gamma-air and beta-air doses calculated will be used to check compliance with the quarterly limits of Spec fication 3.8.3.3. The highest organ dose for a real receptor is determined by summing the dose contribut'on from all real pathways including ground contamination, inhalation, vegetable ingestion (Eor identified garden locat ons), cow and/or goat milk ingest'on (i>> a cow or goat is ident'fied for the ocat.'on), beef ingestion (the be f ingest.'on dose for t'h e locat'on of h.'ghest beef dose Eo" all receptors w.'ll be cons'dered the be E dose for al'eceptozs). The rec ptor hav'ng the highest organ dose is then used to check comol:ance with the quarte ly limits oE Specification 3.8.B.5.

Doses 'ooul.ation r, ~ ~ g ~ 0

~

'For. determining. population doses'to the 50-mi).e population around.the plant, each compass sector is 'broken dovn i@to elements. 'These elements are deEined'n Table 1.5. For each of these sector elements, an average dose is calculated, and then multiplied by the popul.ation in that sector element. Dispersion factors are calculated Eor the midpoint of each sector element (see Table 1.5).

For pooulat'on doses resulting from ingestion, assumed it is conservative'y that all food eaten by the average ind'vidual is grown locally.

The general. equation used for calculating the pooulation dose in a given sector element is:

Dosepop k RATIOP

• POPN

• AGE

• 0 001 ~ DOS P P

where RATIOp = ratio of average to maximum dose for pathway P. (Average ingestion rates are obtained from Regulatory Guide 1.109, Table E-4.)

~ 0.5 for submersioq and ground exposure pathways, a shielding/occupancy factor.

1976p - 16

RETS Manua1 Revision 4 Page 56

~ 1.0 for the inhaLation pathway.

~ 0.515, 0.515, 0.5, and 0.355 for milk, for infant, child, teen and adult, respectively. (Zt is assumed that the ratio of average to max'mum infant mil'k ingestion rates is the same as that for child.)

~ 1.0, 0.90, 0.91, 0.86 for beef ingestion, for infant, child, teen and adult, respectively.

= 1.0, 0.38, 0.38, 0.37: for vegetable ingestion, teen and adult, re'spectively. (lt is assumed that the for.'nfant,'hild, average individual eats no fresh vegetables, only stored vegetables.)

POPS ~ the population of the sector element, persons (Table 1.6).

AGE ~ fraction of the population belonging to each age group.

= 0.015, 0.168, 0.153, 0.665 for infant, child, teen and adult, respec .'ve'y ( ract-ons taken from NUREG/CR-1004, Table 3.39).

0;001 = convers'on from mrem to rem.

DOSEp ~ the dose for pathway P to the maximum individual at the location under consideration, mrem. For ingestion pathways, Poliness:

t;his dose is multiplied by. an average decay correction to

a"Coun't for'ecay as the food is moved. through the food

~~0 distribution. cycle 'This .average. decay:.correction,,'ADC'is 0

as':

~~

ADC = exp(-Kit), for milk and vegetables, where

= decay constant for nuclide i, seconds.

t = dis tr.bution time Eor f ood product unde consideration (from Regulatory Guide 1.109, Table D-l).

~ 1.21K+06 seconds (14 days) for vegetables.

~ 3.46F+05 seconds (4 days) for milk.

exP(-Kit) Xitcb ADC for meat,

( hitcb) where Xi ~ decay constant for nuclide i, seconds.

- 17 1976p

RETS Manual Revision 4 Page 57

= additional distribution time for meat, over and above the time for slaughter to'consumption desc ibed in Section 1.6.3, 7 days (from Regulatory Guide 1.109, Table D-2).

tcb ~ time to consume a whole beef, as descr'bed in Section 1.6.3.

For beef inges ion, the additional factors in the calculation or ADC negate the int gration of the dose term over the period during which a whole beef's consumed, for the calculation oE population dose. This assumes that the max mum individual Ereezes and eats a ~hole beef, but the ave age ind'vidual buys smaller portions at a time.

Population doses are summed over all sector elements to obtain a total

,population dose for the 50-mile population.

1.4 Gaseous Radwas e Treatment System Oceration The gaseous radwaste "" atment system (GRTS) descr.'bed below shall be maintained and operated to ke p releases ALARA.

1.4.1 S stem Description ~ ~

~ ~

.; . A flow diagram Eor."the.GRTS is given in Figure g;3..:.-The system. includes .

'he suhsyste'ms that process and dispose of the gases'..from the train condense 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 stack for dilution and ele'vated release to the atmosphere. The air-ejector off-gas line oE each unit and the stack are continuously monitored by radiation monitors.

1.4.2 Dose Pro'ect'ons In accordanc with Section D.Z of the RLI, dose projections will 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.

If the results oE the dose projection indicate potential doses in excess of the monthly fraction of the annual Technical Specification dose limit, efforts will be'recommended to minimize future releases.

1976p

p8 Np, phd)

,I RETS Manual Revision 4 Page 58 1.5 GASEOUS RELEASES Dose Calculation Equations 1.5 ' Noble as Gamma air dose

.Gamma ai.r doses due to exposure to noble gases will be estimated with the following equation.'y

~ Xim DF (1.11) where:

D~ ~ Gamma air dose, mrad.

Xim ~ i concentration 'of nuclide at location m, pCi/m~. Air concentrations are calculated as described by Equation 1.15.

DF~i dose conversion factor for external gamma mrad/year pe microcurie/m~ (Table 1.4) .

for nuclide i, 1.5.2 Noble as - Beta air dose Beta air doses due to exposure to noble gases will be estimated with the following equation: ~ ~

~ ~ ~ I~

r ~ ~

DS = Xim DFai

~ ~

~~

where:

Dg Beta ai" dose, mrad.

Xim concentration of nuclide i at location m, pCi/m3. Air concentrat.'ons are calculated as described by Equation 1.14.

DFI3i dose conversion factor for external beta mrad/year per microcurie/m3 (Table 1.4).

for nuclide i, 1976p

P'4't j'3 1

RETS ManuaL Revision 4 Page 59 1.5.3 Radioiodine particulate and tritium - Naximum or an dose Organ doses due to radioiodine, particulate and tritium releases are calculated using the following equation:

Dorg m 3 ~ 17Z&8 [ Z (X/Q E Rai + D/Q ROi + X/Q Rli) Qj + (X/Q RPT~ QT1 (1.13 p

where:

Dorg = Organ dose, mrem.

3.17E-08 ~ conversion factor, year/second.

X/Q ~ Relat"'ve conc ntration for location under consideration, sec/m3.

Relative concentrations are calculated as described by Equation 1.15.

Rp: = ingest'on dose factor for pathway P for each ident:fied nuclide i (except tr'ium), m"-mrem/year oe" microcur" e/second. Ingest'on pathways ava.'la'ole for consideration include:

pasture grass-cow-milk ingestion stored feed-cow-milk ingestion pasture grass-goat-'milk feed-goat-milk ingestion ingestion'tored

~ t .pasture grass-beef'ngsstiqn '

~ ~

stored feed-beef inges'tioa'resh

~ ~ ~

leafy vegetable ingestion ,~

stored vegetable ingestion Equations for calculating these ingestion dose factors are given in sections 1.7.1 through 1.7.6.

D/Q = Relative deposition for location unde consideration, m 2.

~ Relative deposition is calculated as described in Equation 1.16.

= Dose factor for standing on contaminated ground, m2-mrem/year per microcurie/second. The equation for calculating the ground plane dose factor is given in Section 1.6.14.

RIi ~ Inhalation dose factor, mrem/year per microcurie/m3. The equation for calculating the inhalation dose factor is given in Section 1.6.13.

~ i 1976p

'A~)

RETS Manual Revision 4 Page 60

~ adjusted release rate for nuclide i for location under consideration, pCi/sec. The initial release rate is adjusted'o account for decay between the release point and the .location, depending on the frequency of wind speeds applicable to that sector. Hence, the adjusted release rate is equal to the actual release rate decayed for an average travel time during the period-9

'~l fj exp(

Qi0- E Xi x/uj) where Qi0 = init'al ave age release rate for nuclide i over the period, pCi/sec.

~ joint relative frequency of occurrence of winds in windspeed

'class j blowing fraction.

toward this exposure point, expressed as a

= ra'diolog.'cal decay constant for nuclide i, sec 1.

= downwind distance, meters.

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

RPT ~ ingestion dose factor:for pathway P for tritium, m2-mrem/year per

~

~

~

microcurie/second. Inges'tion .pathways available for con'sideration same as those. listed abov~ for.Rpi. Fquations for:

~ ~

are the calculat:ng ingestion dqse factors. for tzitiua are given in: '.

sections 1.7.7 through 1.7~1.2.

~ adjusted release rate for tritium for 1'ocation under consideration, pCi/sec. Calculated in th'e same manner as Qi above.

1976p

RETS Manual Revision 4

'Page 61 1.6 GASEOUS RELEASES - Dose Factors 1 ~ 6 ~ 1 PASTURE GRASS where:

6 "(- ',i~'

COW/GOAT-MILK INGESTION DOSE FACTORS (m2-mrem/year per microcuries/second) r(l~( XEten) )

Yp E RCpi Biv(1-exP( Xitb) )

P 106 conversion factor, picocurie/microcur'e.

DFLiao ~ ingestion dose conversion factor for nuclide organ o, mrem/picocurie (Table i, age group a, 1.7).

Uap ~ milk ingestion rate for age group a, liters/year.

Fmi ~ transfer factor for nuclide days/liter (Table 1.8).

i from animal's feed to milk, Qf an'mas consumotion rate, kg/day.

decay constant for nuclide i, seconds 1 (Table 1.8).

tfm ~ transport time from milking to receptor, seconds.

~ ~ ~

~ ~

fp fraction of time animal

~ ~ ~

fraction of activity

~ ~ 4

~,,

spends

~

recta'ined

~

)' ~ ~

~

~

on pasture, dimensionless.

~

on'pasture gra'ss, dimensionless.

~ ~ 'a the effective decay constant, due to radioactive:decay and weathering, seconds 1, equal to Xi + hw.

weathering decay constant for leaf and plant surfaces, seconds tep time pasture is exposed to deposition, seconds.

Yp ~ agricultural productivity by unit area oE pasture grass, kg/m".

Biv transfer factor Eor nuclide i from soil to vegetation, picocuries/'kg (wet weight of vegetation) per picocuries/kg (dry soil) ~

tb ~ time period over which accumulation on the ground is evaluated, seconds.

~ effective surface density of soil, kg/m2.

NOTE: Factors defined above which do not reference a table for their numerical values, are listed in Table 1.9.

1976p

RETS Manual 4 'evision Page 62 1 6 ~ 2 STORED FEEDMOW/GOAT-ilIIK INGESTION DOSE FACTORS RCSi (m2-mrem/year per microcuries/second) 6 (I exP( Xitcsf) tcsf i r(1 e-za( X-~t ~~)) B (1-~~(->'<y)) )

( P Zi Ysf 4~

where:

106 = conversion factor, picocurie/microcurie.

DFLiao ~ ingestion dose conversion factor for nuclide i, age group a, organ o, mrem/picocurie (Table 1.7).

Uap ~ milk ingestion rate for age group a, liters/year.

Fmi ~ t ansfe factor for nuclide i from animal's fe d to milk, days/lite" (Table 1.8).

animal's consumpt'cn rate, kg/day.

fs f act'on of time animal 'spends on stored feed, dimensionless.

decay'onstant for nuclide i, seconds 1 (Table 1.8).

tfm transport time from milking, to receptor seconds.

~ ~

~ ~

tcsf 'time between harves't of stored" feed and consumption by animal,

'econds.

fraction of activity retained on pasture grass, d.'mensionless.

the effective decay constant, due to radioact.ve decay and weathering, seconds 1, equaL to Xi + Xw.

~ weathering decay constant for leaf and plant surfaces, seconds tesf time stored feed is exposed to deposition, seconds' Ysf agricultural productivity by unit area of stored feed, kg/m2.

>iv transfer factor for nuclide i from soil to vegetation, picocuries/kg (wet weight of vegetation) per picocuries/kg (dry soil),

tb time period over which accumulation on the ground is evaluated, seconds.

effective surface density of soil, kg/m .

NOTE: Factors defined above which do not reference a table for their numerical values, are listed in Table 1.9.

1976p 23

RETS Manual Revision 4 Page 63 1.6.3 PASTURE GRASS-BEEF ZNGESTEON DOSE FACTORS - RMPi (m2-mrem/year per microcuries/second)

(1~~P(-witch) )

1P6 DFLiao Uam Ffi gf i tcb. e~( 'hits) r(1-eon(-'Avt ~)) (1-ex~a(-i;t ))

~ ( xp~ Sc

)

where:

106 = conversion factor, picocurie/microcurie.

DFLiao = ingestion dose conversion factor Eor nuclide i, age group a, organ o, mrem/picocurie (Table 1.7).

~ meat ingestion rate for age group a, Rg/year.

~ transfe factor for nuclide i from cow's feed to meat, days/Rg

.(Table 1.8).

= cow's consumot'on rate, '<g/day.

'= decay constant for nuc'ide i, seconds (Table 1.8).

tcb ~ time for receptor to consume a whole beef, seconds.

t's transport time from slaughter. to consumer, seconds.

i fp'.

~ ~ ~ ~ ~ ~

~'.Eractidn of time

~

cow spends:on.~ast;ure, dimensionless:.'

= fraction oE activity retained on pasture grass, dimensionless.

= the effective decay constant, due to ~adioactive decay and weathering, seconds 1, equal to 'Ai + Xw.

= weather'ng decay constant for leaf and plant surfaces, seconds tep = time pasture is exposed to deposition, seconds' Yp agricultural productivity by unit area of pasture grass, Rg/m-.

Biv ~ i transfer factor for nuclide from soil to vegetation, picocuries/Rg (wet weight of vegetation) per picocuries/kg (dry soil).

tb ~ time over which accumulation on the ground is .evaluated, seconds.

~ effective surface density of soil, kg/m2.

NOTE: Factors defined above which do not reEerence a table for their numerical values, are listed in Table 1.9.

24 1976p

RETS Manual Revision 4 Page 64 1 ~6 ' STORED FEED-BEFF ZNGESTTON DOSE FACTORS RMSi (m -mrem/year per microcuries/second)

RMSi ~ 10 6 DFLiao Uam Ffi i tcb (1-exp(-X t g)) r(1-exn(-'Xvt ~)) B: (1-ex (-X t ))

i tcsf ~

Ysf ~E

+

P where:

106 = conversion factor, picocurie/microcurie.

DFLiao = ingestion dose conversion factor for nuclide i, age group a, organ o, mrem/picocurie (Table 1.7).

Uam ~ meat ingestion rate for age group a, Rg/year.

Ffi ~ transfer factor Eor nuclide (Table 1.8).

i from cow's feed to meat, days/Mg Qf = ccw's consumot'on rate, kg/day.

= decay constant Eor nuclide i, seconds - (Table 1.8).

tcb = time for receptor to consume a whole beef, seconds.

ts ~ transport time from slaughter'to consumer, seconds.

~

I 0

~

~ fs ~ fraction of 'time cow spends on stored feed;.dimensionless:

~ ~

0 tcsE = time b'etwedzi.h'arvest of stored feed and consumption by c'ow, seconds.

= fraction of activity retained on pasture grass, dimensionless.

tesE = time stored feed is exposed to deposition, seconds.

Ysf = agricultural productivity by unit area of stored feed, kg/m".

= the efEective decay constant, due to radioactive decay and

~ .

weathering, seconds , equal to 'Ai + Xw.

~ weathering decay constant for leaf and plant surfaces, seconds Biv ~ i transfer Eactor for nuclide from soil to vegetation, picocuries/Rg (wet weight oE vegetation) per picocuries/Rg (dry soil).

tb ~ time over which accumulation on the ground is evaluated, seconds.

~ effective surface density oE soil, kg/m~.

NOTE: Factors defined above which do not reference a table for their numerical values, are listed in Table 1.9.

1976p

RETS Manual

'Revision 4 Page 83 2.3.2 Monthl Anal sis Principal radionuclides will be used to conservatively estimate the monthly cont ibution 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 ooerational source terms, contribute more than 95 percent of the total estimated dose to the total body and the mos" critical organ for both the water and fish ingestion pathways'he organs considered for both water ingestion and fish ingestion are the gastrointestinal tract (GIT), bone, thyroid, and liver.

H-3 Fe-59 Sr-90 I-131 Na-24 Co-58 Zr/M)-95 I-133 Cr-51 Co-60 Mo/Tc-99m C8-134 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

. activities reported (if.;any) for each of the above'0 zadionuclides

..will be .noted; This infopiation will then be 'used in't.he'ollowing calculations:

- 44 1976p

">'~'5'.

r RETS Manual Revision 4 Page 84 2.3.2.1 Water In estion The dose to an individual from ingestion of water is described by the following equation.

20 10 Djk ~

~95 <

7'=1 (DC )ijk Iik, mrem (2.4)

~here:

Djk ~ 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 = conse iative correct'on factor, consider.ng only 20 rad'onuclides.

DCPijk = ingestion dose commitment f'actor for the ith radionuclide for the jth organ for the kth age group, rem/pCi (Table 2.1)

~ monthly activity ingested 'of the ith" r'adioquclide by'.

~ ~

~

the kth age group pCi. ~ ~

~ I r 103 ~ conversion from rem to mrem.

The activity ingested due to drinking water, Iik, is described by:

A~Vi (30) gpCi (2.5)

Z d (7.34 x 1010) where:

Ai ~ activity released of ith radionuclide during the month, pCi.

Vk ~ maximum individual water consumption rate corresponding to the kth age group.

(Adult ~ 2000 ml/d; Child = 1400 ml/d, from Regulatory Guide 1.109) 30 ~ days per month 1976p

~ ~ ~ ~ ~

>I, ~ oea' ~~ ~ <

~ l~

~ S RfTS tlanual 0

Revision 4 i ~ ~ ~ t Page 100 TABLE': 1'. 3 (Sheet 10 of 22) 0 SPLIT 30IHT PERCEtlTAGE FREgUENCIES.OP HItlD SPEED BY HltlD DIRECTION FAlt STABILITY CLASS B (-1.9 < Delta T < -1'.7 C/100H)

BROHtlS FfRRY NUCLEAR PLANT PART 1 OF 2 GROUND LEVEL RELEASf HOOf JAN 1, 77 DfC 31, 79 HI tlD HIND SPfED (MPll)

DIRECTION CALM 0. 6-1.4 1. 5-3. 4 3. 5-5. 4 5. 5-7.4 7. 5-12. 4 12. 5-1tt. 4 18. 5-24. 4 ) 24. 5 TOTAL N 0.0 0.0 0.0 0' 0.01 0.05 0.01 0.01 0.0 O.OB t)HE 0.0 0.0 0.0 0.0 0.01 ~ . ~;0:05 0.01 0.0 0.0 0.07 Nf 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 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 0.01 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 SSH 0.0 0.0 0.0 0.0. 0.0 . 0.0 0.0 0.0 0.0 0.0 SH 0.0 0.0 0.0 0.0 0.0 ,. 0.0 0.0 0.0 0.0 0.0 HSH 0.0 0.0 0.0 0.0 0.02 0.01 0.0 0.0 0.0 0.03 H 0.0 0.0 0.0 0.0 0.01 '.02 0.02 0.01 0.0 0.06 HNH 0.0 0.0 0.0 0.0 0.01 0.03 0.02 0.03 0.0 0.09 NH 0.0 0.0 0.0 0.0 0.01 .:0.04 0.03 0.0 0.0 O.OB NNH 0.0 0.0 0.0 0.0 0.0 ~ .. b.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 25402.0 TOTAL HOURS OF GROUND LEVEL RELEASE 2832.4 TOTAL HOURS OF STABILITY CLASS B 105.1 TOTAL HOURS OF GROUND LEVfL STABILITY CLASS B 163.4 HETEOROLOGICAL .FACILITY:HETEOROLOGICAL FACILITY LOCATED 1 3 KH ESE OF BROHtlS FfRRY tlUCLEAR PLANT STABILITY BASED ON DELTA-T Bf'THEEtl 10;03 AND 45.30 HETERS HItlD DIRECTION MEASURED AT 10.42 HfTER LEVEL HltlD SPEED tlEASURfD AT 10.42 llETER LEVEL EFFLUENT VELOCITY = 12. 60 H/S Fi ')

RETS Manual Revision 4 Page 109 TABLE- 1. 3 (Sheet 'll "of 22)

SPLIT JOINT PERCEtlTAGE FREQUENCIES'OF WIND SPEED BY tlltl0 DIRECTION FOft STABILITY CLASS C (-1.7 <.DELTA-T< -1:5'C/100 M)

BROHNS FERRY NUCLEAR PLAtlT PART 1 Of 2 GROUtlO LCVEL RELEASE ttOOE JAN 1, 77 AEC 31, 79 I

HIND HIND SPEED: (MPH)

OI RECTION CALM 0.6-1.4 1.5-3.4 3.5-5.4 5.5-7.4 '~7.. -12.4 12.5-18.4 10.5-24.4 >--24.5 TOTAL N 0.0 0.0 0.0 0.0 0.01 ~ '.03. 0.0 0.0 0.0 0.04 NNE 0.0 0.0 0.0 0.0 0.01 '0.02 O.n 0.0 0.0 0.03 NE 0.0 0.0 0.0 0.0 0.01 "0.01 0.0 0.0 0.0 0.02 EtlE 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 SSH 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 SH 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 WSH 0.0 0.0 0.0 0.0 0.01 0:01 0.0 0.0 0.0 0.02 .

H 0.0 0.0 0.0 0.0 0.01 0.01 0.01 0.01 0.0 0.04 HtlH 0.0 0.0 0.0 0.0 0.01 0.02 0.02 0.03 0.0 O.QB tlH 0.0 0.0 0.0 0.0 0.01 t).03. ~

0. 02. 0.01 0.0 0.07 NNH 0.0 0.0 0 0

~ 0.0 0.01 0.02 0.03- 0.0 0.0 0.06 1

SUBTOTAL 0.0 0.0 0.0 0.03 0.11 '..17 0.08 0,05 0.0 0.44 TOTAL HOURS OF VALID OBSERVATIOtlS 25482.0 TOTAL HOURS OF GROUND LEVEL RELEASE 2032.4 TOTAL HOURS OF STABILITY CLASS C 259.0 TOTAL HOURS OF GROUND LEVEL STABILITY CLASS C 106.3 METEOROLOGICAL FACILITY:METEOROLOGICAL FACILITY LOCATEO 1.3 KM ESE Of BROHNS FERRY NUCLfAR PLAtlT STABILITY BAS)O Otl DELTA-T BETHEEN 10;03 AtlO 45.30 METERS HIND DIRECTION MEASURfD "AT 10.42 METER LEVEL fFfLUENT VELOCITY = 12.60 M/S:

'7 2 '7 2 n

RETS htanual Revision 4 rr Page 110 TABLE 1.3 (Sheet 12 of 22)

SPLIT JOINT PERCENTAGE FRF+UEHCIES OF HIND SPEED BY l<IWD DIRECTION FOR STABILITY CLASS D (-1.5 ( 'OELTA-T< -0.5'C/100 tt)

BROHNS FERRY NUCLEAR PLANT PART 1 OF 2 GROUND C.EVEL RELEASf h!ODf JAH 1, 77 -'.OEC 31, 79 H!ND l<lttD SPEfO (hiPH)

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 ttttf 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 0.0 0.0 0.0 0.01 0.01 0.01 0.0 0.0 0.0 0.03 EHE E 0.0 0.0 0.0 0.01 0.02 ';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 .'::g.06 0.0 0.0 0.0 0.23 SSH 0.0 0.0 0.01 0.02 0.01 . ..'.01 0;0 0.0 0 0

~ 0.05 SH 0.0 0.0 0.0 0.01 0.01 .0.0 0.01 0.0 0.0 0.03 HSH 0.0 0.0 0.0 0.03 0.03 0:06 0.04. 0.0 0.'0 0.16 H 0.0 0.0 '.0 0.02 0.06

. 6.10 0.09 0.02 0.0 0.29 HWH 0.0 0.0 0.0 0.0 0.03 .. 0:16 0.19 0. 14 0.01 0.53 tN 0.0 0.0 0.0 0.0 0.03 0'.15 0.23 0.10 0.02 0.53 HttH 0.0 0.0 0.0 0.01 0.05 0.25 0. 19 0.04 0.0 0.54 I

SUBTOTAL 0.0 0.0 0.6 0.46 0.67 .. "'.34 '0.92 0.32 0.03 3.80 TOTAL HOURS OF VALID OBSERVATIOttS 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 0 968.6 htfTEOROLOGICAL FACILITY:HETEOROLOGICAL FACILITY LOCATEO 1.3 KH ESE OF BROHWS FERRY ttUCLEAR PLANT STABILITY BASED ON DELTA-T BETHE ftt 10.03 AWO 45.30 hlETERS HlttD DIRECTIOtt MEASURED AT 10.42 htfTER LEVEL EFFLUEHT VELOCITY = )2.60 t4/S 1l'll n Il r

~ ~ 4 A \~

~ I~

RETS Hanual Revision 4

~ ~

Page ill TABLE 1.3 (Sheet 13 of 22)

SPLIT JOItlT PERCENTAGE FRfgUEHCIES OF HIND SPEED flY IIIND DIRECTIOtl FOR STABILITY CLASS E (-0.5(DELTA-T< 1.5'C/100 H)

OROWHS FERRY NUCLEAR PLAttT PART 1 OF 2 GROUND LEVEL RELEASf HODE JAN 1, 77 QEC 31, 79 HIND 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 12.5-1t3.4 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 HHE 0.0 0.0 0.01 0.06 0.07 0.08 0.02 0.0 0 0

~ 0.24 tlf 0.0 0.0 0.01 0.06 0.06 0.05 0.01 0.0 ~

0.0 0. 19

'HE 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 $ .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 0.52 S 0.0 0.0 0.06 0.10 0.09 0.27 0.13 0.01 ( 0' 0.66 SSH 0.0 0.0 0.02 0.02 0.02 0.02 0.01 0.0 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 HSH 0.0 '0.0 0.01 0.05 0 '2 0.03 0;02 0.0 0.0 0.13 H 0.0 0.0 0.01 0.06 0.05 0.05 0.01 0.0 0.0 0.18 HHH 0.0 0.0 0.0 0.01 0.01 0.04 0.02 0.01 0.0 0.09

'NH 0.0 0.0 0.0 0.01 0.02 0.04 0.03 0.01 0.0 0.11 ~

NttH 0.0 0.0 0.0 0.03 0.07 . 0.10 0.02 0.01 0.0 0.23 I

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 METfOROLOGICAL FACILITY:METEOROLOGICAL FACILITY LOCATED 1 .3 KH ESE OF OROWtlS FERRY NUCLEAR PLANT STABILITY BAS)D OH DELTA-TBETHEEH 10.03 At(0 45.30 HETERS HIND DIRECTION HEASURfD AT Tttf 10.42 HETER LEVEL.

HIND SPfED HEASURED AT 10.42.tlfTER LEVEL EFFLUEHT VELOCITY = 12.60 H/S 2125p 72

AETS Hanual Revlslon 4 Page 112 TABLE"I:3.

(Sheet 14 'of:22)

SPLIT JOINT PEACftITAGf FREQUENCIES"OF HltID SPEED BY HltID DIAECTIOW FOR STABILITY CLASS F (1.5 '< DfLTA-T< 4.0 C/100 H)

PART 1 OF 2 GROUND'EVfL RELEASE MODE BAOHNS FERRY WUQ EAR PLAtlT JAII 1, 77 t)EC 31, 79 HIND HltID SPEED (HPII)

OIRfCTION CALM 0. 6-1.4 1.. 5-3. 4 3 ~ 5-5.4 5. 5-7.4 7. 5-12.4 12. 5-1ll. 4 18. 5-24.4 ) 24. 5 TOTAL N 0.0 0.0 0.01 0.06 0.04 " 0.01 0.0 0.0 0.0 0.12 NtIE 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 ENE 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 S

SSH SH 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.04 0.02 0.01 0.0 0.06 0.03 0.0 0.0 0.05 0.04 0.0 0.0

'.0'.0';0

~

0.18 0.11 0.02 0.01 0.0 0.0 0.01 0.0 0.0 0.0 .

0.0 0.0 0.0.

0.0 0.36 0.21 0.01 0.0 HSH H

HWH 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0;0 0.0 0.01 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 0.01 0.0 tN 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 tIWH 0.0 0,0 0.01 0.03 0.02 ~

. 0.01 0.0 0.0 0.0 0.07 SUBTOTAL 0.0 0.0 0.21 0.45 0.27 '.39 0.04 0.01 0.0 1.37 TOTAL HOURS Of VALID OBSERVATIOtJS 25482.0 TOTAL HOURS OF GROUND LEVEL RELEASE 2832.4 TOTAL IIOURS OF STABILITY CLASS F 2385.0 TOTAL HOURS OF GAOUtlO LEVEL STABILITY CLASS F 357.0 HETEOROLOGICAL fACILITY:HETfOAOLOGICALFACILITY I.OCATED 1:.3 KH ESE OF BAOHtIS fEAAY tIUCLEAR PLANT STABILITY BASED OW DELTA-T BETHEEN 10.03 AWO 45.30 HETEAS

. HIND SPEED HEASUAED AT TIIE 10. 42 METE A LEVEL EFfl.UEtlT VEI.OCITY = 12.60 H/5

RETS Hanual Revision 4 Page 113 TABLE 1.3 (Sheet 15 of 22)

SPLIT JOINT PERCENTAGE FREgUENCIES OF HIttD SPEED BY HlttD DIRECTIOtt FOR STABILITY CLASS G,(DELTA-T> 4.0'C/100 tt)

PART 1 OF 2 GROUND LE/EL RELEASE HODE BROHNS FERRY NUCL'EAR PLANT

'AN 1, 77 :.OEC 31, 79 HIND HIND SPEED (MPH)

DIRECTION CALM 0.6-1.4 1.5-3.4 3.5-5.4 5.5-7.4  ?.5-12 .4 12.5-18.4 18.5-24.4 h 24.5 TOTAL N 0.0 0.0 0.02 0.0 ~ ~ 0.0 0.0 0.0 0.0 0.06 NNE 0.0 0.0 0.02 0.03 0.0 0.0 0.0 0.0 0.11 NE 0.0 0.0 0.01 0.0 "0.0 0.0 0.0 0.0 0.02 EttE 0.0 0.0 0.01 0.0 0.0 0.0 0.0 0.0 0.02 E 0.0 0.0 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 '.01 SE 0.0 0.0 0.03 .0.01 ~ '0.02 0.0 0.0 0.0 0.07 SSE 0.0 0.0 0.04 0.03 ~ . Q.06 0.0 0.0 0.0 0.18 S 0.0 0.0 0.01 0.02 ~ 0.01 0.0 0.0 0.0 0.06

. SSH 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 SH HSH 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 H 0.0 0.0 0.0 0.0 0.0 0.0 0.0 .'

Ht(H NH ttNH 0.0 0.0 0.0 0.0 0.0 0.01 0.0 0.0 0.08

'.O .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 0.02 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 25482.0 TOTAL HOURS OF GRONO LEVEL RELEASE 2832.4 TofAL HOURS OF STABILITY CLASS G 694.7 TOTAL HOURS OF GROUD LEVEL STABILITY CLASS G 151.7 HETEOROLOGICAL FACILITY:HETEOROLOGICAL FACILITY LOCATED 1.3 KH ESE OF BROHNS FERRY NUCLEAR PLANT STABILITY BASED ON LAPSE RATE HEASUREO BETHEEN 10.03 AttO 45.30 HETERS HIND SPEED ANO DIRECTION MEASURED AT TttE 10.42 tlETER LEVEL EFFLUENT VELOCITY 12.60 tl/S 2I250 14

RKTS Manual Revision 4 Page 128 Table 1;7 (5 of 8)

LVGESTION DOSE FACTORS (mrem/pCi ingested)

CHILD bone live" t body thyroid sidney gi-Ili H-3 2.03E-07 2.03E-07 2 '3K-07 2.03E-O7 2.03E-O7 2.C3E-C7 2.03E-07 C-14 1.21E-05 2 4?c 2.42K-O6 ~

2.42K-O6 2.42K-C6 2.42K-06 2.42K-06 Va-24 5.80K-06 5.SOE-06 5.SOE-06 5. SOF;06 5.80E-C6 5.SOE-06 5.80E-06 P-32 8.25E-O4 3.86E-05 3.1.8E-O5 O.OCE+00 O.OOK+CO O.COK~CO 2.28E-05 Cr-51 O.OOE+OO O.OOE+00 8.90E-09 4.94i-09 1.35K-O9 9.02K-O9 4.72K-07 Mn-54 C.COKAO 1.07E-05 2.85E-O6 O.COE+CO 3.00E-06 O.OCEANO 8.98i-06 Mn-56 O.COE+00 3.34E-07 7.54E-08 O.OOE+00 4.04i<<07 0. OOK+00 4.84E-05 Fe-55 1.15E-05 6.LOK-06 1.89E-06 O.OOE+OO O.OOE+00 3 45K&6 1.13E-06 Fe-59 1.65K~5 2.67K-05 1.33E-O5 O.OOE+00 O.OCEANO 7. 74K;06 2.78E-05 Co-58 O.OOE+00 1.80E-06 5.51K-06 0. COE+OO O.COK+00 O.OOE+CO 1.05i-05 Co-60 O.COE+OO 5.29E-06 1.56E-05 O.OOE+OO O.COE~OO O.OOK+OO 2.93E-05 Ni-63 5.38E-04 2.SSE-05 1.83E-O5 O.OOE+CO O.COE+CO O.OOK+CO 1.. 94F;06 Vi-65 2.22K-O6 2.09E-07 07 O.OOE+OO O.COE-:CO O.OOE~OO 2. oi-Oa Cu-64 0;OOE+00 2.45K-07 1. 48E-07 O.OOE+00 5.92K-07 0. OOE+OO L. 15F;05 Zn-65 1.37E-05 3.65E-05 2.27E-05 O.OOE+00 2.30E-O5 O.OOK+CO 6.41K-06 Zn-69 4.38E-OS 6.33E-OS 5.85E-O9 O.OOE+00 3.84F.-08 C.OOE+00 3.99E-06 Br-83 O.OOE+00 O.OOE+00 1.71E-07 O.OOE+00 O.COE+00 O.OOE+00 O.OOE+00 Br-84 O.OOE+00 O.OOE+00 1.98E-07 O.OOE+00 O.OOE+OO O.OOE+00 O.OOE+00 Br-85 O.OOE+OO 0;OOE+00 9.12E-09 C.OCE+00 O.OOE+00 O.OOE+00 O.OOE+00

~

~

1 ~

~

Rb-.86 0.00K+CO 6.70E-O5 4.12E-05 0;OOE+00 O.OOE+00 O.OOE+OO 4.31K-06

~ ~ +

Rb +8 0.00E+00 L.90B-07 1. 32K-07. '.OOE+00 0.00K+CO O.OOE+00 9.32K-09 R1<<89 ".

Py g ~

~

~

~ ~

O.OOE+00 l.1.7E-'07 1;04E 07 .0 iPOE+CO'.OOE+00 O.OOE+00 Sr-'89 1.32K-03 O.OOE+00 3.77E-05 O.OOE+00 O.OOE+OQ'.COE+00 1.02K-09'.11E-05 Sr-90 1.70E-02 O.OOE+OO 4.31E-03 0. OOE+00 O.OOE+00 O.OOE+00 2.29E-04 Sr>>91 2.40E-05 O.OOE+OO 9.06E-O7 0. OOE+00 0.00E+00 O.OOE+00 5.30E-O5 Sr-92 9.03E-O6 O.OOE~CO 3.62E-07 O. OCE+00 O.OOE+CO O.OOE+00 1.71K-04 Y-90 4.1.1E-OS O.OOE+00 1.10E-09 0. COE+00 O.OOK~CO O.COK+CO 1.17K-O4 Y-91m 3.82K-LO O.OOE+OO 1.39E-LL O. OOE+OO O.OOE+00 O.OOK+00 7.48E-07 Y-91 6.02E-07 O.OOE+00 1.61E-OS O.OOE+00 O.OOE+00 O.OOE+00 8.02K-05 Y-92 3.60E-09 O.OOE+00 1.03E-LO 0. OOE+00 O.OOE+00 O.OOE+00 1.04E-04 Y-93 1. 14E-08 O.OOE+00 3.13E-LO O.OOE+00 O.OOE+00 O.OOE+00 1.70E-04 Zr-95 1. 16i-07 2.55E-OS 2.27K-OS O.OOE+00 3.65i-08 O.OOE+00 2.66i-05 Zr-97 6 '9K-09 1.01E-09 5.96i-lo O.OOE+00 1.45K-09 O.OOK+00 1,.53i-04.,

Nb-95 2.25i-08 8 '6K-09 6. 26i-09 O.OOE+00 8.23E-O9 O.OOE+00 1.62E-05 Mo-99 O.OOE+OO 1.33E-05 3.29E-O6 O.OOE+00 2.84E-O5 O.OOE+00 1.LOE-05 Tc-99m 9.23E-LO 1.81E-09 3 OOE-08 O.OOE+00 2.63E-CS 9.19E-10 1.03E-06 Tc-101 1.07E-09 1.12E-09 1.42E-OS O.OOE+00 1.91E-OS 5.92E-10 3.56E-09.

RLI-103 7.31K-07 O.OOE+00 2.81E-07 O.OOE+00 1.84E-06 O.OOE+00 L.89E-05 Ru-105 6. 45E-08 O.OOE+00 2.34E-O8 O.OOE+00 5.67E-07 O.OOE+00 4.21E-05 Ru-106 1.17E-05 O.OOE+00 1.46E-06 O.OOE+00 1.58E-05 O.OOE+00 1.82K-04 Ag-LLOm 5.39E-07 3.64E-07 2.91E-07 0.00E+00 6.78E-07 O.OOE+00 4.33E-05 Te-125m 1.14E-05 3.09E:06 1.52E-06 3.20E-06 O.OOE+00 O.OOE+00 1.10E 05 Te-127m 2.89E-05 7.78E-06 3.43E-06 6.91E-06 8.24E-05 O.OOE+00 2.34E-05 Te-127 4.71E-07 1.27E-07 1.01E-07 3.26E-07 1.34E-06 O.OOE+00 1.84E-O5

Reference:

Regulatory Guide 1.109, TabLe E-13 2125p

RETS Manual Revision 4 Page 129 Table 1.7 (6 of 8)

IiVGESTIOiV DOSE FACTORS (mrem/pCi ingested)

CHILD bone liver t body thyroid lcidney g=-1 1 i Te-129m 4.87E-05 1.36E-05 7.56E-06 1.57E-05 1.43E-04 O.CCE+00 5. 94E;05 Te-129 1.348-07 3.74E-OS 3.18E-OS 9.56E-OS 3.92E-07 O.COE+00 8.34E-06 Te-131m 7.2OE-06 2. 49E&6 2. 65E;06 5.12E-06 2.418-05 O.OOE+00 1.018-04 Te-131 S.3OE-OS 2. 3E-08 2.47E-08 6.35E-OS 2.51E-07 O.OOE+OO 4.36E-07 Te-132 1.01E-05 4.47E-06 5.40E-06 6.51E-06 4.15E-05 O.OOE+GO 4.50E-05 I-130 2.92K-06 5 '0E-06 3.04E-06 6.50E-04 S.SZE-06 O.OOE+00 2.76E-06 I-131 1.72E-05 1.,73E-05 9.S3E-06 5.72E-03 2.84E-05 O.OOE+00 1.54E-06 I-132 8.0OE-07 1.47E-06 6.76E-07 6.82E-05 2.25E-06 O.OOE+00 1 ~ 73E-06 I-133 5.92E-06 7.32E-06 2.77E-06 1.36E-03 1.22E-05 O.OOE+OO 2.95E-06 I-134 4.19E-07 7.78E-07 3.58E-07 1.79E-05 1.19E-06 O.OOE+00 5.16E-07 I-135 1.75E-06 3.15E-06 1.49E-06 2.79E-O4 4.83E-06 O.OOEPOO 2.40E-06 Cs-134 2.348-04 3. 84F;04 8.1OE-05 O.OOE+00 1.19E-04 4.27E-O5 2.07E-06 Cs-136 2.35c.-05 6.468-05 4.1SE-05 O.OOE+00 3.448-05 5.13E-O6 2.27E-06 Cs-137 3.27E-04 3.13E-04 4.62E-05 O.OOc~00 1 02c 04 3.57E-05 1.96c.-06 Cs-138 2.2SE-07 3.17E-07 2.018-07 O.OOE+00 2.23E-07 2.40E-OS 1.46c.-07 Ba-139 4.14E-07 2.21E-10 1.20E-OS O.OOE+00 1.93E-10 1.30E-10 2.39E-05 Ba-140 8.31E>>05 7.28E-OS 4.85E-06 ':OOE+00 2.37E-OS 4.34E-OS 4.21E-05 Ba-141 2.00E-07 1.12E-10 6.51E-09 O.OOE+00 9.69E-11 6.58E-10 1.14E-07

. Ba-142 8.74E-OS 6.29E-ll 4.88E-09 0.00E+Og 5.09E-11 3.70E-11 ~

1.14E-09

'.La-140 L.01E-08 3.53E-,09 '1. 1.9E-09 O.OOE+00 O.OOE+00 O.OOE+00 9.84E-OA

~ La-142 5.24E-10 5.2)E-.11 O.OQZ+00 O.OQE+OQ O..QOE+00 3.31E-05 ~

1.67E-10'1.98E-US Ce-141 3.97E-OS 2.94E-09 O.OQE+00 8.68E-09 O.OOE+00 2.47E-05 Ce-143 6 ..9.9E'-09 3.79E-06 5.49E-IO ~ O.OOE+00 1.59E&9 O.OOE+00 5.55E-05

'e-144 2.08E-06 6.52E-07 1.11E-07 O.OOE+00 3.51E-07 O.OOE+00 1.70E-04

• Pr-143 3.93E-OS 1.18E-OS 1 '5E-09 O.OOE+00 6.39E-09 O.OOE+00 4.24E-05 Pr-144 1.29E-10 3.99E-11 6.49E-12 O.OOE+00 2. 11E-11 O.OOE+00 8.59E-08 Nd-.147 2.79E-08 2.26E-OS 1. 75c,-09 O.OOE+00 1.248-08 O.OOE+OO 3.58E-05 M-187 4.29E-07 2.54E-07 1.14E-07 O.OOE+00 O.OOE+00 O.OOE+00 3.57E-05 iVp-239 5.25E-09 3.77E-10 2.65c.-10 O.OOE+00 1.09E-09 O.OOE+OO 2.79E-05

Reference:

Regulatory Guide 1.109, Table E-13 NOTE: The tritium bone dose factor is assumed to be equal to the total body dose factor.

2125p

e TABLE 3.2.A BROMNS FERRY NUCLEAR PLANT RETS Revision Page Manual 163 4

Environmental Radiological Monitoring Program Sampling Locations Map Approximate Indicator (I)

Location Distance or Samples Numbera Station Setter (miles ) Control (C) 'ollectedb 1 Pif-1 NW 13.8 I AP, CF, S 2 P.f-2 NE 10.9. I AP, CF, S 3 PM-3 SSE 8.2 I AP, CF, S 4 L0-7 M 2.1 I AP, CF, S, V 5 RM-1 M 31.3 C AP, CF, S, V 6 RM-6 E 24.2 C AP, CF, S 7 LN-1 N 0.97 I AP, CF, S, V 8 L~f-2 NNE 0.88 I AP, CF, S, V 9 L~f-3 RK 0.92 I AP, CF, S, V

'10 LNW NNW 1.7 I AP, CF, S, V 11 Lf-6 SSW 3.0 1 AP, CF, S, V 12 Farm B NNW 6.8 I if, V 13 Farm Bn N 5.0 I if, V 14 Farm L WE 5.9 I if, V, W 21 Farm W NE 6.8 I 22 Well 06 NW 0.02 I 23 TR'fc 282.6 I PW ~

24 TRM 306.0 12.0d C PM

. ~

" ~

25 Muscle Shoals,. AL W 31.3 I PW 26 TRM 274,9 i9.ld 'I PW I'

~

~ ~, 27$ ' TRM 285:.2. .:.,8 '8d 28 TRM '93'5 0.5d

.":SM':..

SW 29 TRM 305.0 1'1.0d Ce SW 30 TRM 307.52 13.52d CL$ SD 31 TRM 293 ~ 7 0 'd C I CL$ SD 32 TRM 288.78 5.22d I CL$ SD 33 TR'f 277.98 16.02d I CL, SD 34 Farm Be NW 28.8 C 35 Farm 0 E 26.2 C M, 37 TR"f 297.0 3.0 C V'L, SD Milson Reservoir I F (TRM 259-275)

Wheeler Reservoir (TRM 275-349)

Guntersville Reservoir-(TRM 349-424) a See figures 3.1, 3.2, and 3.3

",Sample Codes:

AP ~ Air particulate filter CF ~ Charcoal filter (iodine) S ~ Soil CL ~ Clams SD ~ Sediment F ~ Fish SM ~ Surface Water M ~ Milk V ~ Vegetation PW ~ Public Water W ~ Mell Mater c TRM ~ Tennessee River Mile d Miles from plant discharge (TRM 294)

Also used as a control'for public eater 1977p - 124-

RETS Manual Revision 4 Page 164 TABLE 3.2.B BROWNi S FERRY NUCLEAR PLANT Thermoluminescent Dosimeter Locations Map Approximate Onsi te (On)

Location Distance ~ or Number S tation Sector (miles) Offsite (Off) 1 NW-3 NW 13.8 OH.

2 iK-3 iiE 10.9 Off 3 SSE-2 SSE 8.2 Off 5 W-3 W 31.3 Off 6 E-3 E 24.2 Off 7 N-1 N 0.97 On 8 NNE-1 NNE 0.88 On 9 ENE-1 iiW-2 VK 0 '2 On 10 NNW 1.7 On 38 .'I-2 5.0 Off 39 i'-2 <<3 0.7 On.

40 5.2 Off 41 i'-1 0.8 On 42 iW-2 5.0 Off 43 EK-2 ENE 6.2 Off 44 E-1 E 0.8 On 45 E-2 E 5.2 OEE 46 ESE-1 ESE 0.9 On 47 ESE-2 ESE ~ ~

3.0 Off

'.5

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~ , 48'

..:49

.SE-1 SZ-2

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~ &~ . SE On

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SE 5.4; . OH

.o ',yo30'1 SSE-1 ~ ~

SSE

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5.1  ; Off':..'ff S-1 S 3.1 52 S-2 ~

S 4.8 Off 53 SSW-1 SSW ,3.0 Off 54 SSW-2 SSW 4.4 Off 55 SW-1 SW 1.9 56 SW-2 SW 4,7 OH 57 SW-3 SW 6.0 Off 58 WSW-1 WSW 2.7 OEE 59 WSW-2 WSW 5.1 Off 60 WSW-3 WSW 10.5 Off 61 W-1 1.9 62 W-2 4' Off 63 W-4 32.1 Off 64 WNW-1 3.3 Off 65 WNW-2 ~ 4.4 OH 66 NW-1 2.2 Off 67 NW-2 5.3 OEE 68 NNW-1 1.0 0 69 TLDs TLDs NNW-3 5.2 OEE designated onsite are those lo cated 2 miles or less Erom the plant.

designated offsite are those 1 ocated more than 2 miles from the plant.

-12S-1977p