Text

Radiation Dose Assessment Rept Number 13 Jan-Dec 1997
	ML20217H579
Person / Time
Site:	Peach Bottom
Issue date:	12/31/1997
From:	Basilio J, Mscisz T, Wahl D; PECO ENERGY CO., (FORMERLY PHILADELPHIA ELECTRIC
To:	;
Shared Package
ML20217H570	List: ML20217H563; ML20217H579;
References
	13, NUDOCS 9804300011
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PECO ENERGY COMPAhT PEACH BOTTOM ATOMIC POWER STATION UNIT NOS. 2 & 3 DOCKET NOS. 50-277 AND 50-278 RADIATION DOSE ASSESSMENT REPORT NO.13 JANUARY 1,1997 THROUGH DECEMBER 31,1997 SUBhumu TO THE UNITED STATES NUCLEAR REGULATORY COABHSSION PURSUANT TO FACILITY OPERATION LICENSES DPR-44 & DPR-56 Prepared by:

T. J. Mscisz "

Reviewed by:

D.E. Wahl Approved by:

$. A. Basilio 9804300011 980420 DR ADOCK 0500 7

o TABLE OF CONTENTS I.

INTRODUCTION AND

SUMMARY

II.

STATION LOCATION III.

PEACH BOTTOM LIQUID AND GASEOUS RADWASTE EFFLUFETS IV.

HYDROLOGY AND METEOROLOGY

)

V.

LIQUID AND GASEOUS PATHWAY DOSE MODELS i

VI.

RECEPTOR LOCATIONS AND USAGE FACTORS FOR ANNUAL DOSE EVALUATIONS VII.

CALCULATED AhWUAL DOSES VIII.

METEOROLOGICAL DATA IX.

CONCLUSIONS X.

CORRECTIONS FROM PREVIOUS REPORT XI.

REFFRENCES 1

s

I.

INTRODUCTION AND

SUMMARY

In accordance with the reporting requirements of Peach Bottom ODCM Section 3.10 applicable during the reporting period, this report summarizes the radiation doses due

. to radioactive effluent releases from Peach Bottom Atomic Power Station Units 2 and 3 for the period January 1,1997 through December 31,1907.

Detailed discussion of the methodology utihzed in the report has been provided in a previous report (Ref.1). Only in those cases where the methodology has been changed will it 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 10CFR50 Appendix I Design Objectives. Specifically, the maximum offsite total body dose due to liquid releases was 8.87E-04 mrem; the maximum total body dose due to gaseous releases was 1.28E-03 mrem.

Since PBAPS releases were well within applicable Radioactive Effluent Technical l

Specifications limits and were a small fraction of 10CFR50 Appendix I design objectives, it is concluded that PBAPS releases were within 40CFR190, i

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

i I

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2

TABLE I-1 COMPARISON OF 1997 DOSES RESULTING FROM PBAPS UNITS 2 AND 3 WITH 10CFR50 APPENDIX I DESIGN OBJECTIVES MAXIMUM DOSE DESIGN OBJECTIVES FROM PBAPS (REG. GUIDE 1.109)

DOSE PATHWAY VALUE

% of A A

I Liquid Emuents a.

Dose to total 8.87L04 0.015 3 mrem /yr/ unit body from all pathways b.

Dose to any organ 1.14LO3 0.006 10 mrem /yr/ unit from all pathways II Gaseous Emuents*

a.

Gamma dose in 1.89 & O3 0.009 10 mrad /yr/ unit air b.

Beta dose in air 3.84E-04 0.001 20 mrad /yr/ unit c.

Dose to total 1.28 & O3 0.013 5 mrem /yr/ unit body of an individual d.

Dose to skin of an 1.78E-03 0.006 15 mrem /yr/ unit individual e.

Dose to any organ 8.48E-02 0.283 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 items II (c and d) include noble gas and particulate components.

3

i i

l II.

STATION IACATION 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.

I III.

PEACH BOTTOM LIOUID AND GASEOUS RADWASTE EFFLUFN1'S The release of radioactive materials in liquid and gaseous effluents from PBAPS were reported in the Peach Bottom Atomic Power Station Annual Effluent Release Re. port No. 40 (Ref. 3).

IV.

HYDROLOGY AND METEOROLOGY A. HYDROLOGY Travel times and dilution factors were determined based on the daily Conowingo Pond flows in 1997. Daily Pond flows 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 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 1997, affecting the atmospheric dispersion and the deposition of radionuclides from PBAPS gaseous radwaste releases. This meteorology was used for the I

evaluation of PBAPS Units 2 and 3 gaseous releases.

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LIOUID AND GASEOUS PATHWAY DOSE MODELS The maximum annual doses to individuals in unrestricted areas which 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.

Computer codes, LADTAP and GASPAR, which incorporate the computational models described in Regulatory Guide 1.109 and which were obtained from the NRC staff wem used to perfonn 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 wem calculated using the equations and dose factors provided in the LADTAP computer code.

The gaseous release pathways which were considered included external radiation frorr. the air and ground, inhalation and ingestion of vegetation, meat, cow's milk and goat's milk. 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.

6

VI.

RECEFFOR LOCATION AND USAGE FACTORS FOR ANNUAL DOSE EVALUATIONS A.

Liquid Releases ne annual doses resulting for 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 li%; to occur. The locations and pathways are:

14 cation Number Name Pathways 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 1997. 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 drmking water at Conowingo Dam. The Chester Water Authority withdrew dnnking 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 Releases 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 locations were calculated. These included real locations of dairy pastures and residences in each sector. Meat animal pastures were assumed to co-exist with dairy pastures. A dairy pasture survey was performed in 1997 which determined the pasture closest to EAPS in each sector. There was one herd of milk goats within five mile.c o:.' PBAPS. No gaseo" pathway usage and consumption rates used in these cak ulations changed frot previous years (Ref. 7).

7

FIGURE VI-1 Locations at Which Annual Doses to Individuals Resulting From PBAPS Liquid Radwaste Releases Were Evaluated i

HOLTWOOD DAM be g MT. JOHNSON ISLAND PEACH DOTTOM ATOMIC POWER STATJON O

1

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VII.

CALCULATED ANNUAL DOSES A.

Liquid Releases Tables VH-1 thmugh VII-4 list the calculated annual doses through the various pathways to the maximum individual in the adult, teenager, child and infant age categories as a msult of PBAPS liquid radwaste releases.

The maximum calculated total body dose was 8.87E-04 mrem to the child and occurred at Imation 4, Conewingo Dam. This is 0.015% of the 10CFR50, Appendix I design objective.

The maximum calculated dose to eny organ was 1.14E-03 mrem to the adult

' Liver and occurmd at Location 1. This dose is 0.006% of the 10CFR50 Appendix I design objective.

B.

Gaseous Releases Tables VD-5 and VII-6 list the annual doses to all organs through pathway by age group at the location where a person would receive the largest calculated total body and organ dose respectively resulting from exposure to noble gases, particulates and iodine released from PBAPS.

The maximum calculated total body dose was 1.28E-03 mrem to the child and occurred at a residence 3200 feet NNW fmm the PBAPS building vents. This dose is 0.013% of the 10CFR50 Appendix I design objective.

The maximum calculated organ dose was 8.48E-02 mrem to the infant thyroid and occurred at a diary farm 7400 feet SW fmm the PBAPS building vents.

This dose is 0.283% of the 10CFR50 Appendix I design objective.

The maximum calculated skin dose was 1.78E-03 mrem at a residence 3200 feet NNW from the PBAPS building vents. This dose is 0.006% of the Appendix I design objectives.

The maximum calculated offsite gamma air dose was 1.89E-03 mrad, located 3200 feet NNW of the PBAPS building vents. This dose is 0.009% of the 10CFR50 Appendix I design objective.

The maximum offsite beta air dose is 3.84E-04 mrad, located 3200 feet NNW of the PBAPS building vents. This dose is 0.001% of the 10CFR50 Appendix I design objective.

9

I The location where a person would receive the largest calculated total body dose l

from exposure to PBAPS releases due to non-occupational activities inside the site boundary is at the boat ramp approximately 3300 feet NNW of the PBAPS building vents. The calculated total body dose is 5.74Fe04 mrem and I

calculated skin dose is 8.02Fe04 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 more insignificant dose would result.

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n n

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w t

t h

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c 0 s it e

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le no L

1 d e C

G C

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1 2

3 4

pa M

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l,llllllll\\!Illlll j

SESAEL 5

6 4

4 E

4 4

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0 0

0 E

0 0

7 7

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8 SAW 6

6 4

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g 4

4 4

4 n

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AR Ly 4

4 8

8 0

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8 3

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5 4

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4 4

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8 S

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7 7

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3 8

8 ABP d

6 5

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4 4

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4 4

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6 5

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n

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0 0

A 0

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l:

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M o

o t

t T

T I

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M W

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T h

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1 I

l TABLE Vil-5 ANNUAL DOSES TO ALL ORGANS BY PATHWAY AT LOCATION OF HIGHEST CALCULATED TOTAL BODY DOSE ANNUAL BETA AIR DOSE = 3.84E-04 MILLRADS ANNUAL GAf MA AIR DOSE = 1.89E-03 MILLRADS PATHWAY T. BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN

.........................................+...............................+.....................

PLUME 8 1.28E-03 8 1.28E 03 8 1.28E-03 s 1.28E-03 8 1.28E-03 : 1.28E-03 8 1.28E-03 8 1.78E-03 8

.........+..........+.................................................................+...........

GROUND 8 5.83E 06 8 5.83E-06 8 5.83E 06 8 5.83E-06 8 5.83E-06 8 5.83E-06 8 5.83E-06 8 6.80E-06 8

.........+..........+..........+..........+..........+..........+..........+......................

VECET 8

8 8

ADULT 8 1.03E-04 8 1.84E 04 8 1.22E-03 8 1.39E-05 8 1.09E-05 8 9.41E-06 8 9.92E-06 8 9.41E-06 s

............................... +.......... +.......... +.......... +..................... +.......... +

TEEN 8 1.42E-04 8 2.25E-04 8 1.92E-03 8 1.85E-05 8 1.37E-05 8 1.12E-05 8 1.22E-05 8 1.12E-05 8

.........+..............................+.....................+....................+...........

CHILD : 2.72E-04 8 1.87E-04 8 4.43E-03 8 3.01E 05 8 2.17E-05 8 1.76E-05 : 1,91E 05 8 1.76E-05 8

.........+..........+..........+..........+...............................+..........+..........+

INFANT : 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8

.........+..........+..........+..........+...............................+..........+..........+

MEAT i

s s

s a

s ADULT 8 3.66E-06 8 7.07E-06 8 3.33E-05 8 1.98E-06 8 1.66E-06 8 1.49E-06 8 1.55E-06 8 1.49E-06 8

......... +.......... +.......... +.............................. +..................... +...........

TEEN 8 2.39E-06 8 4.38E-06 8 2.73E-05 8 1.29E-06 8 1.02E-06 8 8.90E 07 8 9.42E-07 8 8.90E-07 8

........................................+................................+..........+...........

CHILD 8 3.35E-06 8 3.22E-06 8 5.00E-05 8 1.60E-06 8 1.25E-06 8 1.08E-06 8 1.14E-06 8 1.08E-06 8

.........+.....................+..........+..........+..........+..........+......................

INFANT 8 0.0 8 0.0 s 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8

.................... +.......... +.......... +..................... +.......... +..................... +

COW MILK s s

s s

ADULT 8 1.23E 05 8 2.21E-05 8 1.24E 04 5 7.11E-06 8 4.73E-06 8 3.50E-06 8 3.91E 06 8 3.50E-06 s

..............................+.....................+.....................+.....................+

TEEN 8 1.72E-05 8 3.00E-05 8 2.23E-04 5 1.09E-05 8 6.73E-06 8 4.56E 06 8 5.41E-06 8 4.56E-06 2

......... +.......... +.......... +......................................... +.......... +.......... +

CHILD s 3.11E-05 8 2.77E-05 8 5.36E-04 8 1.82E-05 8 1.08E-05 8 7.21E-06 8 8.50E-06 8 7.21E-06 8

.........+..........+..........+..........+..........+..........+.....................+...........

INFANT 8 4.83E-05 8 3.16E-05 8 9.89E-04 s 3.25E-05 8 1.67E-05 8 1.09E 05 8 1.33E-05 s 1,09E-05 8

...................+..........................................+..........+..........+...........

GOATMILK ADULT 8 0.0 8 0.0 0,0 0,0 s o,o

0.0 8 0.0 8 0.0 8

.................... +.......... +.......... +.......... +.......... +..................... +.......... +

TEEN 8 0.0 3 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8

...............................+.....................+..........+.....................+...........

CHILD 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8

.........+..........+..........+..........+...........................................+...........

INFANT 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8

.........+..............................+....................................................

INHAL s

s s

i s

s ADULT 8 6.28E-06 8 1.10E-05 8 1.05E 05 8 6.07E-06 8 5.93E-06 8 5.75E-06 8 2.80E 05 8 5.75E 06 8

....................+..........+..........+......................................................

TEEN s 6.41E-06 8 1.14E-05 : 1.32E-05 8 6.23E-06 8 6.04E 06 8 5.79E 06 8 4.41E-05 8 5.79E-06 8

.........+..........+....................+..........+............................................

CHILD 8 5.80E-06 8 7.63E 06 8 1.55E-05 8 5.58E 06 8 5.36E-06 s 5.12E 06 s 3.94E-05 8 5.12E-06 8

.........+..........+..........+..........+................................+......................

INFANT : 3.29E-06 8 3.90E-06 8 8.63E-06 8 3.22E-06 8 3.06E-06 8 2.94E-06 8 3.48E 05 8 2.94E 06 8

................... +.......... +................... +.......... +..................... +...........

15 l

l 1

i

TABLE Vll.6 ANNUAL DOSES TO ALL ORGANS AT LOCATION OF HlGHEST CALCULATED ORGAN DOSE (CHILD THYROID)

ANNUAL BETA AIR DOSE = 1.76E-04 MILLRADS ANNUAL GAMMA AIR DOSE = 5.23E-04 MILLRADS PATHWAY T.BCDY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN

......... +..................... +.......... +..................... +...............................

PLUME s 3.54E-04 s 3.54E-04 8 3.54E 04 8 3.54E-04 s 3.54E-04 8 3.54E 04 s 3.56E-04 8 5.45E-04 8

......... +.......... +..................... +.......... +..................... +......................

GROUND 8 4.59E-06 : 4.59E-06 8 4.59E-06 8 4.59E-06 8 4.59E-06 s 4.59E-06 8 4.59E-06 8 5.52E-06 8

......... +........................................... +.......... +.......... +..................... +

VEGET 8

8 8

ADULT $ 5.75E-05 8 7.40E-05 8 2.57E-04 8 4.19E-05 8 4.52E-05 8 1.64E-03 8 3.58E 05 8 3.58E-05 8

............................... +.......... +..................... +.......... +......................

TEEN 8 7.17E-05 : 8.86E 05 8 4.02E 04 8 4.92F-05 8 5.21E-05 8 1.44E-03 8 4.29E-05 8 4.27E-05 8

......... +.......... +.......... +............................... +.......... +.......... +...........

CHILD s 1.23E-04 8 1.03E-04 9.28E-04 8 7.65E-05 8 7.95E-05 8 2.28E-03 8 6.73E-05 8 6.70E-05 8

......... +.......... +.......... +................................ +.......... +..................... +

INFANT 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 -

8 0.0 8 0.0 8

......... +..................... +..................... +................................ +...........

MEAT s

a s

s ADULT 8 7.00E-06 : 7.29E-06 8 8.05E-06 : 7.32E-06 8 8.38E-06 8 5.18E-04 8 5.68E 06 8 5.67E-06 :

......... +.......... +.......... +..................... +.......... +.......... +.......... +.......... +

TEEN s 4.37E-06 8 4.39E-06 8 6.61E-06 8 4.73E-06 8 5.60E-06 8 3.75E-04 8 3.39E-06 8 3.38E 06 3

...................................................+..........+..........+..........+...........

CHILD 8 5.51E-06 8 4.70E-06 8 1.22E-05 : 5.88E 06 8 6.90E 06 8 5.65E-04 s 4.10E-06 8 4.08E-06 8

......... +.......... +.......... +................................ +.......... +.......... +.......... +

INFANT 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0

.........+...............................+....................+.................................

COW MILK 8 s

s s

a s

ADULT 8 3.45E-05 8 2.85E-05 8 5.02E-05 8 4.94E-05 8 7.43E-05 8 1.11E 02 8 1.34F 05 8 1.33E-05 8

......... +..................... +.......... +.......... +.......... +.......... +.......... +.......... +

TEEN s 5.24E-05 8 3.81E-05 8 9.06E 05 8 8.14E-05 8 1.26E-04 8 1.75E-02 8 1.75E-05 8 1.73E-05 8

.........+..........+..........+..........+..........+..........+..........+..........+..........,

CHILD 8 9.28E-05 8 4.45E-05 8 2.19E 34 8 1.39E-04 8 2.08E-04 s 3.49E-02 8 2.76E 05 8 2.74E-05 8

......... +.......... +.................... +.......... +.......... +.......... +.......... +...........

INFANT : 1.64E-04 8 5.87E-05 8 4.31E-04 8 3.14E-04 s 3.56E-04 8 8.48E-02 8 4.20E-05 8 4.16E 05 8

......... +..................... +........................................... +.......... +.......... +

GOATMILK s' s

s s

s ADULT 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0

...............................+..........+................................+..........+...........

TEEN 8 0.0 8 0.0

o,0 s o,o o,o a o,o

0.0 8 0.0 8

....................+.....................+.....................+..........+..........+..........+

CHILD 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 s o,o 0.0 8 0.0 8

......... +.......... +.......... +.......... +.......... +..................... +.......... +.......... +

INFANT 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8 0.0 8

.............................. +.......... +.......... +.......... +.......... +..................... +

INHAL s

s s

ADULT $ 2.39E.05 8 2.57E-05 8 5.91E-06 8 2.70E-05 8 3.08E 05 8 1.04E 03 8 2.78E-05 8 2.18E 05 :

.........+...........................................+............................................

TEEN 8 2.48E-05 8 2.63E-05 8 7.89E-06 s 2.92E 05 8 3.43E-05 8 1.34E-03 8 3.23E-05 8 2.20E-05 :

.........+................................+.....................+..........+..........+..........+

CHILD : 2.26E-05 8 2.16E-05 8 1.01E-05 8 2.65E-05 8 3.11E-05 8 1.63E 03 s 2.86E-05 8 1.94E-05 8

......... +............................... +................................ +.......... +.......... +

INFANT 8 1.35E-05 8 1.20E-05 8 7.09E-06 8 1.78E-05 8 1.89E-05 s 1.50E-03 8 1.97E-05 : 1.12E-05 8

....................+...............................+.....................+......................

i l

l 16

1 VIII.

METEOROLOGICAL DATA The meteomlogy at the PBAPS site is evaluated by instmments on a meteomlogical tower on the bluff overlooking the plant. It is described in the UFSAR (Ref. 2). All data are summarized using the Pasquill-Gifford system. The following thme tables present the annual summary of hourly meteorological data joint frequency distributions of wind speed, wind direction and atmospheric stability.

I 17

DATA FROM METEOROLOGICAL TOWER FOOT LEVEL 18

L 0879000 4

L 0559700 6

A 791 9

A 484 8

T 1

O O

T T

W 046000 o

W 166000 3

N t

N 1

N N

W 001000 1

W 028100 1

N N

1 W

01 1000 2

W 105400 0

W W

1 W

W W

020000 2

W 065200 3

1 W

000000 0

W 021000 3

S S

W U

W 112000 4

W 020000 2

S S

0 5

0 9

1 1

W 021000 3

W 032000 5

8 S

S T

S E

E E

E F

F YA A

0 S

213000 6

B 0

S 128000 1

D 0

0 1

2 F

3 3

8O S

3 S

3 9

S S

9E A

T A

T 1 M L

L A

E 091 000 o

L A

E 075000 2

/I A

C C

t C

S 1

7T U

S S

1 N

Y R

/

N T

U T

U 2

A I

O I

O LT H

LT H

I E E

523000 0

I E E

086000 4

BE N

S 1

2 BE N

S 1

AF I

T T

S0 N

O O

n 3

I 3

I o

3 T

E 711000 9

3 T

E 360000 9

i C

S 1

1 C

S t

E E

a D

R D

R t

N I

S A

D A

D re 7

7 0

D E

1 60000 7

0 D

E 400000 4

N 1

1 N

w 9

9 0

A 0

A o

9 9

2 2

P 1

1 3

D 3

D

/

E E

c 1

N E

i 3

E P

E 930000 2

E P

E 900000 9

m s /

E S

N 2

3 E

S N

o d

2 W

E W

E A

in 1

T D

t E

N E

N W

B I

m W

W T

7 E

o70000 7

E 310000 4

o 2

F 9

F N

t 1

F N

1 1

t t

1 9

T C

T O

o 3

1 EH EH S

C 3

/

EPN EPN P

1 TFMO TF MO h

I I

c

/

A 0.5. B 0T E

810000 9

A 0.5. B 0T E

270000 9

a N

)

1 T

U N

1 1

T U

N 1

1 e

O t

L3 N

P I

f E3 I

E3 I

S 3

D R

R 3

D T

T E

E

: : S

: :S Y

V 0

N NTTI N

570000 2

NTTI N

133000 7

2 I

OAAD 2

3 OAAD 2

2 A

3 : M P

(RA D

Y D

Y M

EX EDDC EDDC O

TI E SELN SELN C

D F

AROE AROE F

aI D BUHU 00000 BUHU 00000 Y

J tTO SSQ G

l NI YAEE 55555.0 SSQ YAEE 55555.0 R

eER TERRD) 372845 L

TERRD) 372845 L

E M

DDE I MHFEN M

1 1 2 A

MHFEH M

11 2 A

I N

A I P L

T EP L - - - - - 4 T

L T

EP L - - - - - 4 T

E R

I TPM A111112 O

TPM A111112 O

I G

EA BDDNS(

C55555.>

T BDDNS(

C55555.>

T O

O DTT ANNI ANNI C

R FI A TI I O 3728 TI I O

3728 E

P JSD SWWJ 1 1 3WWJ 11 P

l

1 L

0422210 1

L 1332050 4

A 5584 3

A 3931 3 0

T 11 4

T 7523 9

O O

11 3

T T

W 203400 9

W 731320 5

N 23 5

N 34021 1

N N

22 5

W 037700 7

W 931780 8

N 3

4 N

1639 1

12 5

W 070410 2

W 589980 9

N 41 6

N 2317 6

W W

13 5

W 076o00 3

W 387470 9

1 t 3

2945 2

1 3

W 167300 7

W 477500 3

S 1

S 1552 5

W W

1 W

748300 2

W 165300 5

42 8

S 1

0 5

0 0

2 1

N 770500 9

W 096000 5

1421 9

8 S

1 T

S T

s E

E E

E F

F YA C

0 S

019000 0

D G

S 905600 0

D 0

21 4

0 228 4

1 2

F 3

3 8O S

3 S

3 9

S S

9E A

T A

T 1 M L

L A

E 092100 2

L A

E 079800 4

/I A

C S

1 2

C S

375 7

7T U

S S

1 2

1 N

Y R

/

N T

U T

U 2

A I

O I

O LT H

LT H

I E E

292000 3

I E E

499000 2

BE N

S 1

BE N

S 392 6

AF I

1 T

T S0 N

S0 N

O O

n 3

I 3

I o

3 T

E 510000 6

3 T

E 296000 7

i C

S C

S 35 9

t E

E E

E t

N I

D R

s D

R N

I S

A D

0 D

E 030000 3

0 D

E 733000 3

r

. 7 7

N 1

1 N

84 3

ew 9

9 0

A 0

A 1

o 9

9 2

2 P

1 1

3 D

/

E E

ic 1

N E

3 E

P E

21 0000 3

E P

E 350000 8

m

's

/

E S

N 1

1 E

S N

0 0

o d

2 W

E W

E 1

1 t

n 1

T D

i E

N E

N A

W B

I B

I n

W W

o 2

T 7

E 420000 6

E 540000 9

F 9

F N

1 1

F N

13 4

t t

1 9

T O

1 1

3 1

EH EH 8

C 3

/

EPN EPN P

1 TF MO TFMO h

I I

0T 5

762000 5

0T E

380000 1

A 0.5. B c

/

A 0.5. B T

U N

87 6

a N

)

1 T

U N

1 r

O t

L3 N

1 P

I f

E3 I

S 3

D R

R 3

D T

T E

E

: : S

: : S Y

V 0

N NTTI N

405000 9

NTTI N

405000 9

2 I

OAAD 4

4 OAAD 794 0

A 3 : M 1

3 S

(RA D

Y D

Y F

EX EDDC EDDC 0

TI E SELN SELN C

D

- F AROE AROE F

aI D BUHU 00000 BUHU 00000 G

l NI YAEE -

55555.0 YAEE 55555.0 Y

J t TO SSQ SSQ R

eER TERRD) 372845 L

TERRD) 372845 L

E M

DDE I MHFEH M

1 1 2 A

I MHFEH M

112 A

N A

I P L

T EP L - - - - - 4 T

L T

EP L - - - - - 4 T

I TPM A1111 12 O

E R

I TPM A111 112 O

G EA BODNS(

C55555.>

T BDDNS(

C55555 >

T

'0 O

DTT ANNI ANNI

~

O 3728 C

R FI A TI I O

3728 TI I E

P JSD SWWJ 1 1 SWWJ 11 P

1I i

l!I)jill)l1ll l1 Il lll L

1361 820 1

L 1093000 3

A 6321 4

A 32 6

T 132 7

T 42 6

O 11 2

O T

T W

703300 3

W 200000 2

N 471 3

N 1

1 N

W 195620 3

W 860000 4

N 771 7

N 1

2 1

2 W

861 400 9

W 250000 7

N 755 8

N 32 5

W 1

2 W

W 146100 2

W 922000 3

624 3

68 5

2 3

1 W

584100 8

W 991000 9

S 742 4

S 1 7 9

W 1

2 W

1 1

4 341000 8

W 650000 1

S 881 7

S 61 8

0 1

5:

1 0

2 1

W 669100 2

W 140000 5

8 S

75 4

S 21 3

T S

1 T

S E

E E

E F

F YA E

0 S

430100 8

F 0

S 650000 1

D 0

132 6

0 1

2 11 2

F 3

3 8O S

3 S

3 9

S S

9E A

T A

T 1 M L

L A

E 156100 3

L A

E 230000 5

/I A

C S

111 4

C S

1 1

7T U

S S

11 2

S S

1 N

Y R

/

N T

U T

U 2

A O

I O

I LT M

LT H

I E E

67o000 3

I E E

100000 1

BE N

S 86t 6

BE N

S 1

1 AF I

T T

S0 N

O O

n 3

I 3

I o

3 T

E 623000 1

3 T

E 600000 6

i C

S 61 8

C S

1 1

t E

E E

E a

D R

t N

I N

S A

D A

D1 r

E 372000 2

0 D - E 200000 2

0 F

81 0

e 7

7 N

1 1

w 9

9 0

A 1

0 A

o 9

9 2

2 P

1 1

3 D

/

E E

c 1

N E

m W

3 E

E 510000 6

E P

E 100000 1

i s /

E N

4 4

E S

N 1

1 o

d 2

W E

t n

A i

1 T

C T

D E

E N

W B

I B

I m

W W

T 7

E 780000 5

E 700000 7

2 o

F 9

t 1

9 t

F N

4 5

F N

t O

T O

o 3

1 EH EH B

C 3

/

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a IX.

CONCLUSION Table I-1, Introduction and Summary, summanzed 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 I design objective dose limits. All calculated doses were extremely low and well within the 10CFR50 Apoendix I design objective dose limits.

X.

CORRECTIONS FROM PREVIOUS REPORT The previous Peach Bottom Atomic Power Station Radiation Dose Assessment Report (Report Number 12) for the period covering 1996 was found to have seveal minor errors in the summary tables VII-l and VII-2. These errors did not change the maximum doses reponed. All doses were well within the 10CFR50 Appendix I l

design objectives. The corrected tables are included below for reference.

)

l 36

4 464 66 45774 45 74 U 444 00 44404 40 40 ee ee eeeee ee ee 9 2.m.

5 5 G

76 22 581 63 29 64 46099 81 83 414 88 34643 15 42 SESAE L

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1 1 1 1 1 94649 45 45 I

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h 525 44 36.097 09 89 T

91 9 55 34643 1 3 44 P

M O

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XI.

REFERENCES 1.

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

2.

Philadelphia Electric Company, " Peach Bottom Atomic Power Station Units 2 i

and 3, Updated Final Safety Analysis Repon."

3.

Philadelphia Electric Company, " Peach Bottom Atomic Power Station Units 2 and 3, Annual Emuent Releases Report No. 40", January 1,1997 through December 31,1997.

4.

Philadelphia Electric Company, " Peach Bottom Atomic Power Station Units 2 and 3, Radioactive Emuent Dose Assessment", September 30,1976.

5.

U. S. Nuclear Regulatory Commission, Regulatory Guide 1.109, " Calculation of Annual Doses to Man fium Routine Releases of Reactor Effluent for the Purpose of Evaluating Compliance whh 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 Assessmerl Repon 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 Repon No. 5", January 1,1989 through December 31,1989, Table V-2.

8.

Philadelphia Electric Company, " Peach Bottom Atomic Power Station Units 2 and 3, Radiation Dose kmssment Repon No.12", January 1,1996 through D.ecember 31,1996.

j 39

.

ML20217H579

Text

SUMMARY

SUMMARY

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