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PBAPS Units 2 & 3 Radiation Dose Assessment Rept 14 for 1998. with
	ML20206E035
Person / Time
Site:	Peach Bottom
Issue date:	12/31/1998
From:	Doering J, Mscisz T, Wahl D; PECO ENERGY CO., (FORMERLY PHILADELPHIA ELECTRIC
To:	; NRC OFFICE OF INFORMATION RESOURCES MANAGEMENT (IRM)
References
	14, NUDOCS 9905040315
	Download: ML20206E035 (54)
	v • d • e

1 John Doering, Jr.

Ves President A Peach Bottom Atomic Power Staten PECO NUCLEAR ecco cneruv ce-nenv 1848 Lay Road A Unit of PECO Energy Delta, PA 17314-9032 717 456 4000 Fax 717 456 4243 E-maa jdoenng@peco-energycom April 20,1999 Docket Nos. 50-277 50-278 U.S. Nuclear Regulatory Commission Document Control Desk Washington, DC 20555

SUBJECT:

Peach Bottom Atomic Power Station Units 2 and 3,1998 Radiation Dose Assessment Report #14 Gentlemen:

Attached is the Peach Bottom Atomic Power Station Radiation Dose Assessment Report for the period, January 1,1998 through December 31,1998. This report is submitted in accordance with the Peach Bottom Atomic Power Station Off Site Dose Calculation Manual Specification, Section ;

3.10. The report indicates the PBAPS releases were a small fraction of the limits listed in 40 CFR !

190, " Environmental Radiation Protection Standards for Nuclear Power Operations."

l If you have any questions regarding this matter, please call.

1 Sincerely, b AAA4 /SA A blV %f J. Doering Vice President k

JD/ MEW /SCB:jif Enclosure cc: N. J. Sprout, Public Service Electric & Gas R. R. Janati, Commonwealth of Pennsylvania A. J. McMurtray, USNRC Senior Resident inspector R.1. McLean, State of Maryland H. J. Mill 6F, Administrator, Region 1, USNRC l A. F. Kirby, Ill, Delmarva Power INPO Records Center CCN: 99-14038

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9905040315 981231 PDR ADOCK 05000277 .

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PECO ENERGY COMPANY PEACH BOTTOM ATOMIC POWER STATION

UNIT NOS. 2 & 3

, DOCKET NOS. 50-277 AND 50-278 RADIATION DOSE ASSESSMENT REPORT NO.14 JANUARY 1,1998 THROUGH DECEMBER 31,1998 SUBMITTED TO THE UNITED STATES NUCLEAR REGULATORY COMMISSION PURSUANT TO FACILITY OPERATION LICENSES DPR-44 & DPR-56 ,

PECO ENERGY COMPANY PEACII BOTTOM ATOMIC POWER STATION UNIT NOS. 2 & 3

- DOCKET NOS. 50-277 AND 50-278 RADIATION DOSE ASSESSMENT REPORT NO.14 JANUARY 1,1998 TIIROUGH DECEMBER 31,1998 SUBhuiTED TO TIIE UNITED STATES NUCLEAR REGULATORY COMMISSION PURSUANT TO FACILITY OPERATION LICENSES DPR-44 & DPR-56

Prepared by:

M J. Mscisz U Reviewed by:

D.E. Wahl Approved by: MO M

d. A. Basilio

Peach Bottom Atomic Power Station 1998 Radiation Dose Assessment Report TABLE OF CONTENTS Section Title Page I Introduction And Summary 2 II Station IAcation 4 III Peach Bottom Liquid And Gaseous Radwaste Effluents 4 IV Hydrology And Meteorology 4 V Liquid And Gaseous Pathway Dose Models 6 VI Receptor Locations And Usage Factors For Annual Dose 8 Evaluations VII Calculated Annual Doses 11 VIII Meteorological Data 24 IX Conclusions 52 X References 52 1

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Peach Bottom Atomic Power St:. tion 1998 Radi: tion Dose Assessment Report L INTRODUCTION AND

SUMMARY

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1 l

In accordance with the reporting requirements of Peach Bottom ODCM Section 3.10.3 l applicable during the reporting period, this report summanzes the radiation doses due to radioactive effluent releases from Peach Bottom Atomic Power Station Units 2 and 3

' for the period January 1,1998 through December 31,1998. j i

Detailed discussion of the methodology utilized in the report has been provided in a l previous report (Ref.1). Only in those cases where the methodology has been changed willit be discussed in detail.

The radiation doses due to the release of radioactive materials during the reporting period were well below 10CFR50 Appendix I and 40CFR190 limits. A comparison of the calculated doses to the appropriate limits is presented on Table I-1, Comparison of Doses Resulting from PBAPS Units 2 and 3 with ODCM and 10CFR50 Appendix I Design Objectives. Specifically, the maximum effsite total body dose due to liquid releases was 2.40E-03 mrem; the maximum offsite total body dose due to gaseous {

releases was 7.32E-02 mrtm. l l

Since PBAPS releases were well within applicable Radioactive Effluent Technical l Specifi:ations limits and were a small fraction of ODCM and 10CFR50 Appendix I design objectives, it is concluded that PBAPS releases were within 40CFR190, ,

" Environmental Radiation Protection Standards for Nuclear Power Operation" limits.

2

e Peach Bottom Atomic Power Station

!?98 Radirtion Dose Assessment Report TABLE I-1 COMPARISON OF 1998 DOSES RESULTING FROM PBAPS UNITS 2 AND 3 WITH ODCM REQUIREMENTS MAXIMUM DOSE ODCM

~

FROM PBAPS REQUIREMENTS

. DOSE PATHWAY VALUE % of A A I Liquid Emuents

a. Dose to total 2.40E-03 0.04 3 mrem /yr/ unit body fmm all pathways

b. Dose to any organ 2.55E-03 0.01 10 mrem /yr/ unit from all pathways II Gaseous Emuents*

a. Gamma dose in 7.25E-02 0.36 10 mrad /yr/ unit air

b. Beta dose in air 1.42E-02 0.04 20 mrad /yr/ unit

c. Dose to total 7.32E-02 0.73 5 mrem /yr/ unit body of an individual

d. Dose to skin of an 9.80E-02 0.33 15 mrem /yr/ unit individual

e. Dose to any organ 1.50E-01 0.50 15 mrem /yr/ unit

. from all pathways

10CFR50 Appendix I specifies dose from noble gases only for categories II (a, b, c and d). PBAPS doses presented for category II (c and d) items include noble gas and particulate components.

3 l

Pesch Bottom At:mic Power Stttion 1998 Raditti:n Dise Assessmezt Report IL STATION LOCATION Peach Bottom Atomic Power Station is located on the western shore of Conowingo Pond in York County, Pennsylvania. The station, two boiling water reactors (3458 MWt), is described in the Updated Final Safety Analysis Report (Ref. 2). Conowingo Pond is the receiving stream for liquid radwaste effluents.

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HL PEACH BOTTOM LIOUID AND GASEOUS RADWASTE EFFLUENTS The release of radioactive materials in liquid and gaseous effluents from PBAPS are reported in the Peach Bottom Atomic Power Station Effluent Release Report No. 41 (Ref. 3).

IV. HYDROLOGY AND METEOROLOGY A. HYDROLOGY Travel times and dilution factors were determined based on the daily Conowingo Pond flows in 1998. Daily Pond flowg were reviewed to determine a mean monthly Pond flow. Each daily flow value was assigned to one of three Pond flow regimes (Ref. 4). The resulting daily travel times and dilution factors were then averaged to determine a monthly mean travel time and dilution factor for each receptor location.

The travel times and dilution factors for those locations in the Conowingo Pond, where the highest doses were calculated, are listed in Table IV-1 for each monthly flow regime.

B. METEOROLOGY Section VIII describes in detail the meteorology in the PBAPS region during 1998, affecting the atmospheric dispersion and the deposition of radionuclides from PBAPS gaseous radwaste releases. This meteorology was used for the evaluation

- of PBAPS Units 2 and 3 gaseous releases.

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Peach Bottom Atomic Power Station 1998 Radiation Dose Assessment Report V. LIOUID AND GASEOUS PATHWAY DOSE MODELS The maximum annual doses to individuals in unrestricted areas that could result from the effluent releases from PBAPS were calculated according to the guidelines in USNRC Regulatory Guide 1.109 (Ref.5) and the models described therein. NRC computer codes, LADTAP and GASPAR, which incorporate the computational models described in Regulatory Guide 1.109, were used to perform the liquid and gaseous dose calculations respectively.

. The liquid release pathways which were considered in making these calculations included drinking water, aquatic foods, shoreline usage, swimming, and boating. All pathways were calculated using the equations and dose factors provided in the LADTAP computer code. ,

E All gaseous release pathways considered included external radiation from the air and ground, inhalation and ingestion of vegetation, meat, cow's milk and goat's milk as applicable. The inhalation and ingestion pathways were evaluated for the adult, teenager, child, and infant age groups. The dose calculation at each receptor was done in two parts - a dose component resulting from the off-gas stack and one from the building vents. These doses were then summed to yield a total dose for each pathway and organ.

The dose models to be used in future reports will be bounding evaluations as opposed to individual receptor evaluations as described beMw.

Liauld Pathway Model To Be Used In Future Reports:

This new bounVg method will calculate total body, organ, and skin doses due to liquid releases as they would be if all pathways (e.g., drinking water, aquatic foods, shoreline usage, swimming, and boating) existed at the location just below the plant discharge. Usage factors would be adjusted to the highest of the four (4) current locations for each pathway for consetvatism. The table below indicates the current and bounding usage factors for this location. The discharge location shoreline width factor will also be increased (from 0.1 to 0.2, the highest factor of the 4 locations currently evaluated).

- Current Method Bounding Method Factor Adult Itsn Child Difg_ntt Adult Teen Child Infant Eating Fish (kg/yr) 21 16.9 6.9 0 21 16.9 6.9 0 Drinking Water (1/yr) 0 0 0 0 730 510 510 330 Shoreline Use (hr/yr) 0 0 0 0 325 325 14 0 Swimming (hr/yr) 0 0 0 0 280 280 0 0 Boating (hr/yr) 120 120 67 0 325 325 67 0 6

Peach Bottom Atomic Power Station i 1998 Rzdistion Dose Assessment Report If the results of these bounding doses were found to be above the ODCM annual limits, then a pathway-specific analysis would be performed at each of the 4 locations to verify compliance with the ODCM. The computer program LADTAP will continue to be used to determine doses due to liquid radioactive releases. This method was used for this report in addition to the current method for comparison. Current method results are listed in Tables VII-l through VII-4. Bounding method results are indicated in Table VII-5. Table VII-6 provides a summary of both methods for comparison. Table

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VII-7 indicates the fractional increases of the bounding method over the current method.

Gaseous Pathway Model To Be Used In Fr.ture Resorts:

Doses due to gaseous releases will be evaluated at the location with the highest calculated annual average X/Q and D/Q. All pathways will be assumed to exist at the highest X/Q and D/Q location in order to determine a bounding annual dose value. If, in the unlikely event that this calculated dose value were to be above any ODCM limit, a location-specific analysis would then be performed that would reflect the appropriate pathways for each individual location in order to verify ODCM compliance. The annual average X/Q and D/Q values will continue to be determined for all identified receptor locations. The computer program GASPAR will continue to be used to determine doses due to gaseous radioactive releases. Using this method, the resulting doses for 1998 were slightly higher due to the addition of several ingestion pathways at the highest X/Q and D/Q location but resulted in the same identified location as did the individual location method.

4 7

Peach Bottom Atomic Power Station 1998 Radiation Dose Assessment Report VI. RECEI'rOR LOCATION AND USAGE FACTORS FOR ANNUAL DOSE EVALUATIONS A. Liauld Releases The annual doses resulting from PBAPS liquid radwaste releases were calculated at various locations on Conowingo Pond. The locations are shown in Figure VI-1. These locations were selected because they represent areas where the listed pathway activities are most likely to occur. The locations and

. pathways are:

Location Name Pathways Number 1 1500 feet below discharge boating, fish 2 Chester Water Authority drinking water 3 Glen Cove boating, fish, shoreline recreation, swimming 4 Conowingo Dam drinking water, fish, boating The City of Baltimore (location 5) withdrew drinking water from Conowingo Pond only one (1) day in 1998. Since Conowingo Pond represents only a small

' fraction of the water supply for the City of Baltimore, any doses resulting from this pathway are much smaller than those estimated from drinking water at Conowingo Dam. The Chester Water Authority withdrew drinking water from Conowingo Pond approximately 40 percent of the year. Usage factors were adjusted accordingly. No other liquid pathway usage and consumption rates used in these calculations changed from previous years (Ref. 6).

B. Gaseous Releasi

- In order to assure that the location of the maximum off-site annual dose to each pathway resulting from PBAPS radioactive gaseous effluents was identified, annual doses at several (136) locations were calculated. These included real locations of dairy pastures and residences in each sector. Meat animal pastures were assumed to coexist with dairy pastures. A dairy pasture survey was performed in 1998 which determined the pasture closest to PBAPS in each sector. There was one herd of milk goats in the W sector within five miles of PBAPS. No gaseous pathway usage and consumption rates used in these calculations changed from previous years (Ref. 7).

8

Peach Bottom Atomic Power Station 199'd Radiation Dose Assessment Report FIGURE VI-1 Locations at Which Annual Doses to Individuals Resulting From PBAPS Liquid Radwaste Releases Were Evaluated O

HOL w 00

%e g MY. JOHNSON ISLANO it'*Je*EIM" STATJ ON

-= = STATE LINE BROAD CREEK

- CONOWIN00 DAM O

9

Peach Bottom Atomic Power Station 1998 Radiation Dose Assessment Report VIL CALCULATED ANNUAL DOSES A. Liauld Releases e

Tables VII-l through VII-4 list the calculated annual doses through the various pathways to the maximum individual in the adult, teenager, child, and infant age categories in each of the four receptor locations as a result of PBAPS liquid radwaste releases.

The maximum calculated total body dose from all liquid pathways was 2.40E-03 mrem to the child and occurred at Location 4, Conowingo Dam. This is 0.04% of the 10CFR50, Appendix I design objective. Using the previously mentioned bounding analysis method, a value of 6.98E-03 mrem to a child was calculated.

The maximum calculated dose to any organ from all liquid pathways was 2.55E-03 mrem to the adult thyroid and child liver, both of which also occurred at Location 4. This dose is 0.01% of the 10CFR50 Appendix I design objective. Using the previously mentioned bounding analysis method, a value of 6.75E-03 mrem to the infant liver was calculated.

B. Gaseous Releases Tables VII-8 and VII-9 list the annual offsite doses to all organs through all pathways by age group at the offsite location where a person would receive the largest calculated total body and organ dose respectively resulting from exposure to noble gases, particulates, and iodines released from PBAPS.

The maximum calculated offsite total body dose was 7.32E-02 mrem to the infant and occurred at a residence 2900 feet NW from the PBAPS building vents. This dose is 0.73% of the 10CFR50 Appendix I design objective.

The maximum calculated offsite organ dose was 1.50E-01 mrem to the infant thyroid and occurred at a residence 2900 feet NW from the PBAPS building vents. This dose is 0.50% of the 10CFR50 Appendix I design objective.

The maximum calculated offsite skin dose was 9.80E-02 mrem to a child at a residence 2900 feet NW from the PBAPS building vents. This dose is 0.33% of the Appendix I design objectives.

a maximum calculated offsite gamma air dose was 7.25E-02 mrad, located

. >00 feet NW of the PBAPS building vents. This dose is 0.36% of the 10CFR50 Appendix I design objective.

10

Peach Bottom Atomic Power Station 1998 Radiation Dose Assessment Report The maximum offsite beta air dose is 1.42E-02 mrad, located 2900 feet NW of the PBAPS building vents. This dose is 0.04% of the 10CFR50 Appendix I design objective.

The location where a person would receive the largest calculated total body dose from exposure to PBAPS releases due to non-occupational activities inside the site boundary is at the boat ramp approximately 2100 feet NNW of the PBAPS building vents. The calculated total body dose is 7.27E-02 mrem and calculated skin dose is 8.47E-02 mrem assuming continuous occupancy. If the

. shoreline recreational usage factor (325 hours0.00376 days <br />0.0903 hours <br />5.373677e-4 weeks <br />1.236625e-4 months <br /> per year) were used, a smaller dose would result. Table VII-10 lists doses at this location.

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F Peach Bottom Atomic Power Station 1998 Radiation Dose Assessment Report m :LE Vll-5 MAXIMUM 1998 CALCULA1cd k at \L DOSES DUE TO LIQUID RADWASTE RELEASES ASSUMING ALL P;M% AYS DOWNSTREAM FROM THE PLANT DISCHMiGE (LOCATION 1)

ANNUAL ADULT DOSES BY PATHWAY:

. PATHWAY SKIN BONE LIVER TOTAL BODY THYROID KIDNEY LUNG GI-LLI FISH 0 4.82E-04 1.39E-03 7.43E-04 1.21E 04 8.81E 04 1.47E-04 9.63E-04 DRINKING 0 8.70E-06 4.71E-03 4.70E-03 4.68E-03 4.69E-03 4.68E-03 4.76E-03

. SHORELINE 4.82E-04 3.87E-04 3.87E-04 3.87E-04 3.87E-04 3.87E-04 3.87E 04 3.87E-04 SWIMMING 0 3.73E-06 3.73E-06 3.73E-06 3.73E-06 3.73E-06 3.73E-06 3.73E-06 EOATING 0 2.04E 06 2.04E-06 2.04E-06 2.04E-06 2.04E-06 2.04E-06 2.04E-06 TOTAL: 4.82E-04 8.84E-04 6.49E 03 5.83E-03 5.19E-03 5.97E-03 5.22E-03 6.11E-03 ANNUAL TEENAGER DOSES BY PATHWAY:

-PATHWAY SKIN BONE LIVER TOTAL BODY THYRolD KIDNEY LUNG GI-LLI

' FISH 0 4.65E-04 1.37E-03 6.48E-04 9.32E 05 8.22E-04 1.25E-04 6.56E-04 DRINKING 0 7.69E-06 3.32E-03 3.31 E-03 3.30E-03 3.31 E-03 3.30E-03 3.35E-03 SHORELINE 4.82E-04 3.01E-04 3.01E-04 3.01E-04 3.01E-04 3.01E-04 3.01E-04 3.01E-04 SWIMMING 0 3.73E-06 3.73E-06 3.73E 06 3.73E-06 3.73E-06 3.73E-06 3.73E-06

' COATING 3.97E-04 2.04E-06 2.04E-06 2.04E-06 2.04E-06 2.04E-06 2.04E-06 2.04E-06 TOTAL: 8.79E-04 7.79E-04 5.00E 4.27E-03 3.70E-03 4.44E-03 3.73E-03 4.31E-03 l ANNUAL CHILD DOSES BY PATHWAY:

PATHWAY' SKIN BONE LIVER TOTAL BODY ' THYROID KIDNEY LUNG GI-LLI FISH 0 5.17E-04 1.11E-03 6.16E-04 7.70E-05 6.49E-04 1.02E 04 2.61E-04 )

DRINKING 0 2.00E-05 6.35E-03 6.35E 03 6.31E 03 6.33E-03 6.31 E-03 6.36E-03 /

. SHORELINE 2.08E-05 1.76E-05 1.73E-05 1.73E-05 1.73E-05 1.73E-05 1.73E-05 1.73E-05 i EOATING 0 4.45E-07 4.45E 07 4.45E-07 4.45E-07 4.45E-07 4.45E-07 4.45E-07 TOTAL: 2.08E45 5.55E-04 7.48E-03 6.98E 03 6.40E 03 7.00E-03 6.43E-03 6.64E-03 l

ANNUAL INFANT DOSES BY PATHWAY:

PATHWAY SKIN BONE LIVER TOTAL BODY THYROID KIDNEY LUNG GI-LLI DRINKING 0 2.10E-04 6.75E-03 6.47E-03 6.20E 03 6.50E-03 6.22E-03 6.51 E-03 )

TOTAL: 0 2.10E-04 6.75E-03 6.47E-03 6.20E-03 6.50E-03 6.22E-03 6.51 E-03 i

16 I

-)

I l

! l Peach Bottom Atomic Power Station l 1998 Radittion Dose Assessment Report 1

! TABLE Vil-6 COMPARISON OF LOCATION - SPECIFIC ANALYSIS TO BOUNDING ANALYSIS METHODS f mrem / year j BOUNDING ANALYSIS METHOD

\

LUNG GI-LLI I DjiLN BONE LIVER TOTAL BODY THYROID KIDNEY

/

8.84E 04 6.49E-03 5.83E-03 5.19E 03 5.97E-03 5.22E-03 6.11 E-03 f* ADULT 4.82E-04 Ingestion Drinking Drinking Drinking Drinking Drinking Drinking P .thway Shoreline l 1 1 1 1 1 Location 1 1 1 7.79E 04 5.00E 03 4.27E-03 3.70E-03 4.44E-03 3.73E-03 4.31 E-03 TEEN 8.79E-04 Ingestion Drinking Drinking Drinking Drinking Drinking Drinking P:thway Shoreline 1 1 1 1 Lccation 1 1 1 1 5.f,5E-04 7.48E 03 6.98E-03 6.40E-03 7.00E 03 6.43E-03 6.64E-03 CHILD 2.08E-05 Ingestion Drinking Drinking Drinking Drinking Drinking Drinking Pathway Shoreline 1 1 1 1 1 Location 1 1 1 2.10E-04 6.75E-03 6.47E-03 6.20E-03 6.50E-03 6.22E 03 6.51 E-03 INFANT 0 Drinking Drinking Drinking Drinking Drinking Drinking Drinking Pithway N/A 1 1 1 1 1 Lccation 1 1 1 CURRENT LOCATION - SPECIFIC METHOD BONE kjyJS TOTAL BODY THYROlD KIDNEY LUNG GI-LLI aliLN 5.10E 04 2.08E-03 1.86E-03 2.55E 03 1.91 E-03 1.67E 03 1.96E 03 ADULT 2.70E 04 Drinking Drinking Drinking Drinking Drinking Drinking Ptthway Shoreline Ingestion 4 4 4 4 4 4 Lccation 3 3 4.98E-04 1.59E-03 1.36E-03 1.17E-03 1.41 E-03 1.18E-03 1.37E 03 TEEN 2.70E-04 Drinking Drinking Drinking Drinking Drinking Drinking

!. P thway Shoreline Ingestion 4 4 4 4 4 4 Lccation 3 3 5.18E-04 2.55E 03 2.40E 03 2.21E-03 2.40E-03 2.22E-03 2.28E 03

CHILD 1.18E 05 Drinking Drinking Drinking Drinking Drinking Drinking Prthway Shoreline ingestion 4 4 4 4 4 L cation 3 1 4 2.16E-03 2.15E-03 2.14E-03 2.15E 03 2.14E-03 2.16E-03 0 5.71E-05 INFANT _ Drinking Drinking Drinking Drinking Drinking i P.sthway N/A Drinking Drinking 4 4 4 4 4 Ltcation 4 4 l 17 I

Peach Bottom Atomic Power Station 1998 Radiation Dose Assessment Report TABLE Vll 7 FRACTIONAL INCREASES IN 1998 ANNUAL DOSES DUE TO LIQUID RADWASTE RELEASES WHEN A BOUNDING ANALYSIS IS USED NOTE: This table indicates the fractional increase in calculated 1998 annual doses when using the bounding analysis method. In no case was there a decrease in calculated dose over the previous location-specific method.

SKIN BONE LIVER TOTAL BODY THYROID KIDNEY LUNG GI-LLI 1.88 1.84 3.18 l 3.15 l 2.04 l 3.16 l 3.12 l 3.15 l l ADULT l l l 3.43 1.66 3.22 l 3.19 l 3.16 l 3.19 l 3.16 l 3.17 l l TEEN l l l 1.86 1.36 2.97 l 2.93 l 2.90 l 2.94 l 2.90 l 2.91 l l CHILD l l l N/A l 4.10 l 3.13 l 3.01 l 2.90 l 3.02 l 2.90 l 3.01 l llNFANT l 18

I i

I t

I l Peach Bottom Atomic Power Station i

1 1998 Radirtion Dose Assessm:nt Report j TABLE Vll 8 ANNUAL DOSES TO ALL ORGANS BY PATHWAY AT LOCATION OF HIGHEST CALCULATED TOTAL BODY DOSE l

ANNUAL HETA AIR DOSE = 1.42E-02 MILLRADS ANNUAL GAMHA AIR DOSE = 7.25E-02 MILLRA03 T. BODY GI-TRACT HONE LIVER K1DNEY THYR 0!D LUNG SKIN PATHWAY PLUME l 4.91E-02.___.

.________.__....__. l 4.91E-02 l 4.91E-02 l 4.91E-02 l 4.91E-02 l 4.91E-02

...__...____.....-___...___.._________.______. l 4.92E-02 l 6.78E-02

__.__________. .._______.l i GROUND j 1.22E-04 l 1.22E-04 l 1.22E-04 l 1.22E-04 l 1.22E-04 l 1.22E-04 l 1.22E-04 l 1.43E-04 l 1 l ] l VEGET l l l l ADULT l E.20E-03 l 6.26E-03 l 5.13E-05 l 6.20E-03 l 6.20E-03 l 6.79E-03 6.19E-03 6.19E-04 l

=.....___.......

... _____....... ___.........._.__________....____....__________._...._____.= )

TEEN l 7.40E-03 l 7. 4 0 E-0 3 l 8 . 31 E-0 5 l 7.40E-03 l 7.40E-03 l 7.92E-03 l 7.40E-03 l 7.40E-03 l '

l

....CHILD l 1.16E-02 l 1.17E-02 l 2.01E-04 l 1.16E-02 l 1.16E-02 l._____.____.-___..___........____.

1.25E-02 l 1.16E-02 l 1.16E-02 l ,

l 0.0 l 0.0 l 0.0 { 0.0 l 0.0 l 0.0 l INFANT l 0.0

......___.._ .._____. l_________..............__

0.0 .____...._______........___. _____ ....__________.

l l l l l l MEAT l ADULT l 9.83E-04 9.90E-04 l 1.78E-06 l 9.82E-04 l 9.82E-04 l 1.12E-03 l 9.82E-04 l 9.82E-04 TEEN l 5.86E-04 l 5.90E-04 l 1.50E-06 l 5.86E-04 l 5.86E-04 l 6.87E-04 l 5.86E-04 l 5.86E-04 l

...______.......____....... ___.._________.........._.__________... _______.._________....______-. l CHILD j 7.09E-04 l 7.10E-04 l 2.82E-06 l 7.00E-04 l 7.08E-04 l 8.60E-04 l 7.07E-04 l 7.07E-04 l ;

l

!NFANT l 0.0 l 0.0 l 0.0 l 0.0 [ 0.0 l 0.0 l 0.0 l 0.0 l I l l l l COW MILK l l l l ADULT l 2.31E-03 l 2.32E-03 l 1.46E-05 l 2.32E-03 l 2.33E-03 l 5.95E-03 l 2.31E-03 l 2.31E-03

..______l .... 3.01E-03 l 3.02E-03 l 2.68E-05____..__l .....__.__

3.03E-03 l...___

3.05E-03 l 8.85E-03 l 3.00E-03 l 3.00E-03 l TEEN CHILD l 4.77E-03 l 4.76E-03 j 6.54E-05 l 4.79E-03 l 4.82E-03 l 1.68E-02 l 4.74E-03 l 4.74E-03 l THFANT l 7.24E-03 l 7.21E-03 l 1.32E-04 l 7.31E-03 l 1.32E-03 l 3.64E-02 l 7.20E-03 l 7.20E-03 l

_____.___......_____......_____.....__.......____ ....__________.._________.. ________...._______.l l l l l GOATMILK l l ADULT l 4.71E-03 l 4.72E-03 l 2.94E-05 l 4.73E-03 4.74E-03 1.05E-02 l 4.70E-03 l 4.70E-03 l TEEN l 6.14E-03 l 6.15E-03 l 5.39E-05 l 6.17E-03 l 6.19E-03 l 1.55E-02 l 6.13E-03 l 6.13E-04 l 1 CHILD j 9.72E-03 l 9.70E-03 l 1. 32E-04 l 9.75E-03 l 9,79E-03 l 2.89E-02 l 9.68E-03 l 9.68E-Oi l INFANT l 1.48E-02 l 1.47E-02 l 2.63E-04 l 1.49E-02 l 1.49E-02 l 6.15E-02 l 1.47E-02 l 1.47E-02 l

-._____ .... _...___...... ___.............______ ......._______._______.......___ ....__________.l INHAL l l l l l ADULT l 3.79E-03 ) 3.79E-03 l 3.95E-06 { 3.79E-03 1l 3.79E-03l l4.33E-03 l 3.79E.03 3.78E-04 l TEEN l 3.81E-03 l 3.81E-03 l 5.58E-06 l 3.81E-03 l 3.82E-03 l 4.53E-03 l 3.82E-03 l 3.81E-01 l CHILD l 3.37E-03 l 3.37E-03 l 7.66E-06 l 3.37E-03 l

. . _____.......___..__ ..____..__________...._____..._. __. ___...________.____3.38E-03 l 4.31E-03 l 3.38E-03 l 3.37E-03 l INFANT l 1.44E-03 l 1.94E-03 l 4.96E-06 l 1.94E-03 l 1.94E-03 l 2.80E-03 l 1.94E-03 l 1.94E-03 l f NOTE: The abovw location has the meat, cow milk, and goat milk pathways included in thw calculation j These pathways do not currently wxist at this as a demonst ration o f t he bounding analysis method.

location.

l TOTALS DUE TO ALL PATHWAYSt GI-TRACT RONE LIVER K1DNEY THYR 0!D LUNG SKIN l T. BODY '

6.72E-02 6.73E-02 4,93E-02 6.72E-02 6.73E-02 7.79E-02 6.72E-02 0.59E-02 Adult 8.89E-02 Teen 7.02E-02 7.03E-02 4.94E-02 7.02E-02 7.03C-02 0.67E-02 7.02E-02 4.96E-02 7.95E-02 1.13E-01 7.93E-02 9.80E-02 Child 6.90E-02 7.95E-02 7.94E-02 Infant 7.32E-02 7.31E-02 4.96E-02 7.34E-02 7.34E-02 1.50E-01 7.31E-02 9.18E-02 l

19

Peach Bottom Atomic P0wer Station 1998 Radiation D0se Assessment Report TABLE Vil-9 ANNUAL DOSES TO ALL ORGANS AT LOCATION OF HIGHEST CALCULATED ORGAN DOSE (THYROID)

(NOTE: Same as Table Vll-8 for 1998)

ANNUAL HETA AIR DOGE = 1.42E-02 MILLRADS ANNUAL GAMMA AIR DOSE = 7.25E-02 MILLRADS GI-TRACT BONE LIVER K!DNEY THYROID LUNG SKI N FATHWAY T. BODY l 4.91E-02 j 4.91E-02 l 4.91E-02 l 4.91E-02 l 4.91E-02 l 4.91E-02 l 4.92E-02 l 6.78E-02 l

".L1UME 1ROUND l 1.22E-04 l 1.22E-04 l 1.22E-04 l 1.22E-04 l 1.22E-04 l 1.22E-04 l 1.22E-04 l 1.43E-04 l 1

/EGET l l l l i ADULT 6.20E-03 6.26E-03 l 5.13E-05 l 6.20E-03 6.20E-03 6.79E-03 l 6.19E-03 6.19E-03 l i

TEEN l 7. 4 0E-0 3 l 7. 4 8E-03 l 8.31E-05 l 7.40E-03 l 1.40E-03 l 7.92E-03 l 7.40E-03 l 7.40E-03 l

......___.__...____..________. .______ ...._________..__= ----_.________........____.. ._______..

CHILD l 1.16E-02 l 1.17E-02 l 2.01E-04 l 1.16E-02 l 1.16E-02 l 1.25E-02 l 1.16E-02 l 1.16E-02 l INFANT l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 { 0.0 l

......___....__.....+....____......._-__ .._...___........._.....__ --_ _= .__._____......___.__..

MEAT l l l l l

ADULT j 9.83E-04 l 9.90E-04 1.78E-06 9.82E-04 9.82E-04 l 1.12E-03 9.82E-04 l 9.82E-04 l

..__...__.......__....__........__..__....+_. __ =.._...._____.__________ ___....___....___..__.

TEEN l 5.86E-04 l 5.90E-04 l 1.50E-06 l 5.86E-04 l 5.86E-04 l 6.87E-04 l 5.86E-04 l 5.86E-04 l CHILD l 7.09E-04 l 7.10E-04 l 2.82E-06 l 7.08E-04 l 7.08E-04 l 8.60E-04

.. ....__....______..__________.._________...__....._.__________.__ l 7.07E-04 l 7.07E-04 l INFANT l 0.0 l 0.0 l 0.0 l 0.0 { 0.0 l 0.0 l 0.0 l 0.0 l row MILK l l l ADULT l2.31E-03 l 2.32E-03 l 1.46E-05 2.32E-03 l 2.33E-03 5.95E-03 2.31EA.3 2.31E-03 l

_________.J_____ . __.___ .__ ..............__________.__....____...________._______ .......___.._.

TEEN l 3.01E-03 l 3.02E 03 l 2.68E __ ...l 3.03E-03 l 3.05E-03 l 8.85E-03 l 3.00E-L3 l 3.00E-03 l

____..__..____..____.__________.______-05 CHILD l 4.77E-03 l 4.76E-03 l 6.54E-05 l 4.79E-03 l 4.82E-03 l 1.68E-02 l 4.74E-03 l 4.74E-03 l INFANT l 7.24E-03

......___.________ l 7.21E-03 l 1.32E-04 l 7.31E-03

..._________.__________.. l 7.32E-03

________... l 3.64E-02

__..........___ l 7.20E-03 l 7.20E-03 l GOATMILK l l l l ADULT 4.71E-03 4.72E-03 2.94E-05 l 4.73E-03 l 4.74E-03 l 1.05E-02 l 4.70E-03 4.70E-03 TEEN l 6.14E-03 l 6.15E-03 l 5.39E-05 l 6.17E-03 ) 6.19E-03 l 1.55E-02 l 6.13E-03 l 6.13E-03 l CHILD l 9.72E-03

______......._ l 9.70E-03

....... .... l 1.32E-04 l ....____..

___.__________._ 9.75E-03 _______

l 9.79E-03......___..._.________...

l 2.89E-02 l 9.68E-03 l 9.68E-03 _______.l INFANT l 1.40E-02 l 1.47E-02

_____.....__..______.____ ..___.l _____..

2.63E-04 l 1.49E-02 l 1.49E-02 l 6.15E-02

....__...___.__________._ l 1.47E-02 l 1.47E-02 l INHAL l l l l l ADULT l 3.79E-03 l 3.79E-03 } 3.95E-06 l 3.79E-03 3.79E-03 4.33E-03 3.79E-03 3.78E-03 l TEEN l 3.81E-03 l 3.81E-03 l 5.58E-06 l 3.81E-03

___.._...._________..__________.._________... l 3.02E-03

.....__.____ ....l ...________...._______._..

4.53E-03 l 3.82E-03 l 3.81E-03 __ ....l CHILD l 3.37E-03 l 3.37E-03 l 7.66E-06 l 3.37E-03 l 3.38E-03 l 4.31E-03 l 3.30E-03 l 3.37E-03 l INFANT l 1.94E-03 l 1.94E-03 j 4.96E-06 l 1.94E-03 l 1.94E-03 l 2.00E-03 l 1.94E-03 l 1.94E-03 l f0TE: The above location has the meat, cow milk, andThesw goat pathways milk pathways included in the calculation 50 a demonst rat ion o f t hw bounding analysis method. do not currently exact at this ocation.

(OTALS DUE TO ALL PATHWAYS l LIVER KIDNEY THYROID LUNG SKIN l T.HODY GI-TRACT BONE Adult b.72E-02 6.73E-02 4.93E-02 6.72E-02 6.73E-02 7.79E-02 6.72E-02 0.59E-02 keen 7.02E-02 7.03E-02 4.94E-02 7.02E-02 7.03E-02 8.67E-02 7.02E-02 8.89E-02 6.90E-02 7.95E-02 4.96E-02 7.94E-02 7.95E-02 1.13E-01 7.93E-02 9.80E-02 phild Bnfant 7,32E-02 7.31E-02 4.96E-02 7.34E-02 7.34E-02 1.50E-Ol 7.31E-02 9.18E-02 20

Peach Bottom Atomic Power Station 1998 Radiation D0se Assessment Report l

f TABLE VII-10

LOCATION OF LARGEST CALCULATED TOTAL BODY DOSE DUE TO NON-l l

t OCCUPATIONAL ACTIVITIES INSIDE THE SITE BOUNDARY (BOAT RAMP)

I i ANNUAL BETA AIR DOSE . 1.65E-02 MILLRADS l ANNUAL GAMMA AIR DOSE _ 8.58E-02 MI LLRADS l

1 GI BONE LIVER KIDNEY THYR 010 LUNG SKIN PATHWAY T.HODY

___..... ..________ .___-TRACT _______.__________.._________.__________.. ....____._ ..______.. ____ ....

! rLUME l 5.81E-02 l 5.8iE.02 l 5.01E-02 l 5.01E_02 l 5.01E-02 l 5.01E.02 l 5.83E 02 1 8.00E.02 l GROUND j 1.40E-04 l 1.40E-04 l 1.40E-04 l 1.40E-04 l 1.40E-04 l 1.40E-04 l 1.65E-04 l

____...__.11.40E-04.....____...__........__________.__________._______....__________._________..__________.

l l l l [

vEGET l l l ADULT l 0.0 ) 0.0 l 0.0 l 0.0 0.0 l 0.0 l 0.0 l 0.0 l TEEN l 0.0 l 0.0 l 0.0 l 0.0 1 0.0 l 0.0 l 0.0 l 0.0 l

____...__........___.___.____....._______.._________ .__ ...........____ ... _________........___4 CHILD l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 1 0.0 l 0.0 l INFANT l 0.0 [ 0.0 l 0.0 l 0.0 l 0.0 l 0.0 { 0.0 l 0.0 l l l l l l HEAT ADULT 0.0 0.0 l1 0.0 l 0.0 l 0.0 1 0.0 l 0.0 0.0 l TEEN l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 l CHILD l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 l INFANT l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 _...__._..____..____.____._.______.......___.... l 0.0 l l l l l 00W HILK l l l[ 0.0 l 0.0 ADULT l 0.0 ..__._ _ [ 0.0 0.0 l 0.0 -_ .

l 0.0 .

0.0 l

CHILD l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 -- ..____ l 0.0 l 0.0 ......_________.....______. l 0.0 l INFANT l 0.0 l 0.0 l 0.0 l 0.0 - l 0.0 l 0.0 l 0.0 7l 0.0 l GOATM1LK l l l l l l l

ADULT 0.0 l 0.0 0.0 [ 0.0 l 0.0 l 0.0 l 0.0 [ 0.0 l TEEN l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 l CHILD l 0.0 l 0.0 [ 0.0 l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 l INrANT l 0.0 0.0 l 0.0 l 0.0 l 0.0 l 0.0 l 0.0 l

_____.__.. __.._____.1 0.0_______.__.1 ._________.___ .._...._______.__.____..____._..._____ .__________.

l l j INHAL l l l 4.47E-03 l l 4.47E-03 l 4.48E-03 l 5.10E-03 l 4.40E-03 4.47E-03 i

ADULT l 4.47E-03 l

. .J .4 . 5 6 E - 0 6 TEEN l 4.50E-03 l 4.50E-03 l 6.45E-06 l 4.50E-03 l 4.51E-03 l 5.34E-03 l 4.51E-03 l 4.50E-03 l CHILD l 3.90E-03 l 3.90E-03 l 8.86E-06 l 3.98E-03 l 3.99E-03 l 5.01E-03 l 3.99E-03 l 3.98E-03 l (NFANT l 2.29E-03 l 2.29E-03 l 5.74E-06 l 2.29E-03 l 2.29E-03 l 3.30E-03 l 2.30E-03 l 2.29E-03 l NOTE: Since this is on on-site location for recewational use only, no ingestion pathways are assumed r

f or t his location. Continuous occupancy was assumed in the dose dwtwrmination.

TOTALS DUE TO ALL REMAINING PATHWAYS i

BONE LIVER KlDNEY THYROID LUNG SK1N

! T. BODY GI-TRACT Adult 6.21E-02 6.27E-02 5.82E-02 6.27E-02 6.27E-02 6.33E-02 6.72E-02 8.46E-02 6.27E-02 6.27E-02 6.27E-02 6.36E-02 6.27E-02 8.47E-02 Teen 7.27E 5.82E-02 Child 6.22E-02 6.22E-02 5.82E-02 6.22E-02 6.22E-02 6.33E-02 6.22E-02 8.41E-02 6.05E-02 5.82E-02 6.05E-02 6.05E-02 6.15E-02 6.05E-02 8.25E-02

Infant 6.05E-02 l

1-21

f Puch Bottom Atomic Power Station 1998 Radirtion Dose Assessment Report VIII. METEOROLOGICAL DATA l l

The meteorology at the PBAPS site is evaluated by instruments on a meteorological tower on the bluff overlooking the plant and is described in the UFSAR (Ref. 2). All data are summarized using the Pasqtill-Gifford system. The following three tables present the j l annual summary of hourly meteorological data joint frequency distributions of wind speed, wind dimetion, and atmospheric stability at the three elevations of concern.

Table Description 1-VIII-l Primary Meteorological Tower - 33' Elevation VIII-2 Primary Meteorological Tower - 75' Elevation VIII-3 Primary Meteorological Tower - 320' Elevation l

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l Pt.c.cti Bottom Atomic Power Station 1998 Radiation Dose Assessment Report l ,

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! 111

Peach Bottom Atomic Pmer Station 1998 Radi: tion Dose Assessmert Report IL CONCLUSIONS

- A. Table I-1, Introduction and Summary, summarized the maximum calculated annual doses resulting from Peach Bottom Atomic Power Station Units 2 and 3 routine liquid and atmospheric radwaste releases and how they compare to the 10CFR50 Appendix 1 design objective dose limits. All calculated doses were extremely low and well within the 10CFR50 Appendix I design objective dose limits.

1 B. A bounding analysis has shown that calculated doses using this method results in l slightly higher reported doses but remains acceptable. This method will be used in future reports.

L REFERENCES ,

1. Philadelphia Electric Company, " Peach Bottom Atomic Power Station Units 2 and 3, Radiation Dose Assessment Report No. 5", January 1,1989 through December 31, 1989.

2. PECO Energy Company, " Peach Bottom Atomic Power Station Units 2 and 3, i l

Updated Final Safety Analysis Report."

PECO Energy Company, " Peach Bottom Atomic Power Station Units 2 and 3, l 3.

Effluent Releases Report No. 41", January 1,1998 through December 31,1998. l

4. Philadelphia Electric Company, " Peach Bottom Atomic Power Station Units 2 and 3, '

Radioactive Effluent Dose Assessment", September 30,1976.

5. U. S. Nuclear Regulatory Commission, Regulatory Guide 1.109, " Calculation of Annual Doses to Man from Routine Releases of Reactor Effluent for the Purpose of Evaluating Compliance with 10 CFR Part 50, Appendix I", Revision 1, October, 1977.

6. Philadelphia Electric Company, " Peach Bottom Atomic Power Station Units 2 and 3, Radiation Dose Assessment Report No. 5", January 1,1989 through December 31, 1989, Table V-1.

7. Philadelphia Electric Company, " Peach Bottom Atomic Power Station Units 2 and 3, Radiation Dose Assessment Report No. 5", January 1,1989 through December 31, e 1989, Table V-2.

8. PECO Energy Company, " Peach Bottom Atomic Power Station Units 2 and 3, Radiation Dose Assessment Report No.13", January 1,1997 through December 31, 1997.

52

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SUBJECT:

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SUBJECT:

SUMMARY

f4 r= ~ Q .@- C

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= V) m == 0 @ A E c r o O O r= 0 N O e m , O .= e w O m c

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