ML20112B606

PBAPS Units 2 & 3 Annual Radiological Environ Operating Rept 53,Jan-Dec 1995

ML20112B606
Person / Time
Site:	Peach Bottom
Issue date:	12/31/1995
From:	PECO ENERGY CO., (FORMERLY PHILADELPHIA ELECTRIC
To:
Shared Package
ML20112B603	List: ML20112B602 ML20112B606
References
NUDOCS 9605220501
Download: ML20112B606 (107)

Text

.

I. g

, . , .+.

~ Docket No: 50-277 E50-278 +

PEACH?BOTTOMiLATOMIC POWER 1 STATION UNITS 2 and!3' '

LAnn'ual/R'adiblogical '

i Environ mental;; Operating :R eport!

ReportL#53:

tisJanuary Through L31: December::1995 tl

, g 1

f

. 1 Prepared By PECO Nuclear.

Ia (Jnit of PECO Energy 965 Chesterbrook Blvd.: ,

Wayne, PA 19087-5691 May 1996 ee8' $888A 3I88$3n R PDH

Docket No: 50-277 50-278 PEACH BOTTOM ATOMIC POWER STATION UNITS 2 and 3 Annual Radiological Environmental Operating Report Report #53 1 January Through 31 December 1995 Prepared By A

_N V

PECO Nuclear a Unit of PECO Energy 965 Chesterbrook Blvd. .

Wayne, PA 19087-5691 May 1996 1

hD 050 0 17 R PDR

Docket No: 50-277 50-278 PEACH BOTTOM ATOMIC POWER STATION UNITS 2 and 3 Annual Radiological Environmental Operating Report Report #53 1 January Through 31 December 1995 Prepared By 4

V PECO Nuclear a Unit of PECO Energy 965 Chesterbrook Blvd.

Wayne, PA 19087-5691 May 1996 J

i r

l 1

TABLE OF CONTENTS l 1. Summary and Conclusions . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1 II. I nt ro d u ctio n . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3 A. Obje ctive s . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3 l

B. I m ple m e ntatio n . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3 Ill. Program Description . . . . . . . . . . . . . . . . . . . . . . . . . . . . ............ 5

A. Sample Collection . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5 B. Data inte rpretation . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7 C. P rog ram Exception s . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 8 D. P rog ram C hange s . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 8 IV. Results and Discussion . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 10 A. Aquatic Environ me nt . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 10

1. Su rface Wate r . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 10

2. Drinking (Potable) Water . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 10

3. Fi s h . . . . . . . . . . . . . . . . . . . . . . . ..................... 11

4. Sedi me nt . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 11 B. Atmospheric Environment . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12

1. Ai rbo rne . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12

n. Air Particulates . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12

b. Airborne lodine . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 13

2. Te rre strial . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 13

a. Milk . ........................................ 13 C. Ambient Gamma Radiation . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 13 V. Refe re n ce s . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 14 i

i I

..l.

Appendix A -

Radiological Environmental Monitoring Report Summary Appendix B -

Sample Designation and Locations Appendix C -

Data Tables and Figures - Primary Laboratory i Appendix D -

Data Tables and Figures - OC Laboratory  !

Appendix E -

Synopsis of Analytical Procedures Appendix F -

Quality Control - EPA Intercomparison Program Appendix G -

PBAPS Surveys 1

t p-1

- ii -

! l. Summary and Conclusions

)

l This report on the Radiological Environmental Monitoring Program conducted for the Peach Bottom Atomic Power Station (PBAPS) by PECO Nuclear covers the period 1 January 1995 tnrough 31 December 1995. During that time period,966 analyses were performed on 863 samples.

Surface water samples were analyzed for concentrations tritium and gamma emitting nuclides. No fission or activation products were found. Tritium activities ,

detected were consistent with thoes o,bserved in other years.

~

l Drinking (potable) water samples were analyzed for concentrations of gross beta i (soluble and insoluble fractions), tritium, and gamma emitting nuclides. No fission or activation products were found. Gross beta and tritium activities detected were consistent with those observed in other years.

1 The remaining sample media representing the aquatic environment included fish and sediment samples. These media were analyzed for concentrations of gamma emitters. Fish samples showed no measurable effects from the operation of PBAPS. Sediment Location 4J, located below the discharge, showed the activation product Co-60 which was attributable to PBAPS operations. Cesium-137 activity was found at all locations and was consistent with data from previous  ;

years. The dose to a teenager's skin from the sediment pathway was calculated to be 1.37 E-03 mrem /yr which represents less than 0.01% of the allowable fraction of 10 CFR 50, Appendix l limits.

The atmospheric environment was divided into two parts for examination: airborne and termstrial. Sample media for determining airborne effects included air particulates and air iodine samples. Analyses performed on air particulate samples l included gross beta and gamma spectrometry. The results from both analyses l were consistent with results from the previous years. Furthermore, no notable differences between control and indicator locations were observed. These findings 1 indicate no measurable effects from the operation of PBAPS.

High sensitivity lodine-131 analyses were performed on weekly air samples. All results were less than the minimum detectable activity.

Examination of the terrestrial environment was accomplished by analyzing milk samples for concentrations of lodine-131 and gamma emitters. Results from all analyses were consistent with those from previous years and showed no indication of PBAPS effect.

l l

I I

! 71

. . . - - _ = - - - - - - . - _ . .. .. -.

i Ambient gamma radiation levels were measured quarterly throughout the year. All  ;

measurements were below 10 mR/std. month and consistent with those measured  ;

in previous years.  ;

i The operation of the Station had no measurable effect on the environs surrounding Peach Bottom.  !

i i,

i l

l

-2

II. Introduction Peach Bottom Atomic Power Station (PBAPS) is located along the Susquehanna River between Holtwood and Conowingo Dams in Peach Bottom Township, York County, Pennsylvania. The initialloading of fuelinto Unit 1, a 40 MWe (net) high temperature, gas-cooled reactor, began on 5 February 1966, and initial criticality was achieved on 3 March 1966. Shutdown of Peach Bottom Unit 1 for decommissioning was on 31 October 1974. For the purposes of the monitoring program, the beginning of the operational period for Unit 1 was considered to t=

5 February 1966. A summary of the Unit 1 preoperational monitoring program was presented in a previous report m. PBAPS Units 2 and 3 are boiling water reactors each with a power output of approximately 1102 MWe. The first fuel was loaded into Peach Bottom Unit 2 on 9 August 1973. Criticality was achieved on 16 September 1973, and full power was reached on 16 June 1974. The first fuel was loaded into Peach Bottom Unit 3 on 5 July 1974. Criticality was achieved on 7 August 1974, and full power was first reached on 21 December 1974.

Preoperational summary reports ** for Units 2 and 3 have been previously issued and summarize the results of all analyses performed on samples collected from 5 February 1966 through 8 August 1973.

A. Objectives The objectives of the REMP are:

1. To identify, measure, and evaluate existing radionuclides in the environs of PBAPS site and any fluctuations in radioactivity levels which may occur.

2. To monitor and evaluate ambient radiation levels.

3. To determine within the scope of the program, any measurable quantity of radioactivity introduced to the environment by the operation of PBAPS.

B. Implementation implementation of the stated objectives is accomplisned by identifying significant exposure pathways, establishing baseline radiological data of media within those pathways, and monitoring those media during plant operation to assess plant effects (if any) on man and the environment.

In order to achieve the stated objectives, the current programs include the following analyses on samples collected:

1

1. Concentrations of beta emitters in drinking (potable) water, and air particulates.

2. Concentrations of gamma emitters in surface and drinking (potable)  !

water, air particulates, milk, fish, and sediment.

3. Concentrations of tritium in surface and drinking (potable) water.

(

4. Concentrations of I-131 in air and milk.

5. Ambient gamma radiation levels at various site environs.

l l

I i

i 4

[r~

I l

111. Program Description A. Sample Collection This section describes the collection methods used to obtain environmental samples for the PBAPS REMP in 1995. Samples for the PBAPS REMP were collected for PECO by Normandeau Associates, RMC Environmental i Services Division. (RMC). Sample locations and descriptions can be found j l in Table B-1 and Figures B-1 through B-3, Appendix B.

Aauatic Environment The aquatic environment was examined by analyzing samples of surface

! water, drinking water, fish, and sediment. Surface water from two locations (1LL and 1MM) were collected week!y by automatic sampling equipment. l l Drinking water from two locations (4L and 61) were collected weekly from a l tank at each location Buth surface and drinking water samples were each  !

composited into separate modhly samole for analysis. Two quarts of water  ;

are removed from the tank each week and placed into a clean two-gallon j polyethylene bottle to form a monthly composite. Control locations were 1 LL a n d 6 1.

Fish samples comprising the flesh from two groups, catfish (bottom feeder) and smallmouth bass, largemouth bass, or bass (predator) were collected l semiannually at two locations: 4 (indicator) and 6 (control) using several methods such as trapnet, seine or electroshocking.

Sediment samples composed of recently deposited substrate were collected semiannually at three locations: 4J, 4T (indicators), and 6F (control) using one of two methods, determined by the depth from which the sediment was obtained. In water greater than 4 feet deep, sediment was collected by either a Ponar or Ekman Grab with a surface area of 81 square inches. In shallow water (1-4 feet), sediment was collected by scooping up mud with a plastic bucket.

Atmospheric Environment The atmospheric environment was examined by analyzing airborne and l terrestrial samples. These consisted of air particulates, airborne lodine, and

! milk. Air particulate and air iodine samples were collected and analyzed l weekly from five locations (1B,1Z,2,3A, and 22G1). The control location was 22G1. Air samples were obtained using a vacuum sampler, glass fiber and charcoal filters, respectively. The filters were replaced weekly and sent l

j

5- 1 4

h to the laboratory for analysis. The vacuum samplers were run continuously

at approximately 1 cubic foot per minute. I Milk samples were collected from five locations (A, G, J, N, and O) monthly j

from December through March and biweekly April through November.

j Additionally, samples from six locations (B, C, D, E, L, and P) were collected j'

quarterly. Locations A, B, C, and E were controls. Milk samples were obtained by removing two gallons from the dairyman's bulk tank after mixing.

The sample from each location was therefore a composite of all the milk collected from the dairy herd (from 1 to 3 milkings). The milk was scooped 3 from the agitated bulk tank and placed in new plastic containers.

4 4

Ambient Gamma Radiation l Direct radiation measurements were made using Panasonic 801 calcium sulfate (CaSO4 ) thermoluminescent dosimeters (TLD). The TLD locations j were placed on and around the LGS site as follows:

4 A site boundary rina consisting of thirteen locations (1L,1 A,2,11,1C, i 1 J, 1 F, 40, 1NN,1H,1G,1B, and 1E) near and within the site perimeter representing fencepost doses (i.e., at locations where the

• doses will be potentially greater than maximum annual off-site doses) from LGS releare.'

i '

An intermediate distance rina consisting of nineteen locations (15,22,44,32, 45,14,17, 31 A, 4K, 23, 27, 48, 3A, 49, 50, 51, 26, 68, and 42) extending

~

to approximately 5 miles from the site designed to measure possible exposures to close-in population.

The balance of eight locations (43, 5,16, 24, 46, 47,18, and 19) representing control and special interests areas such as population centers, 4

schools, etc.

j The specific TLD locations were determined by the following criteria:

j 1. The presence of relatively dense population;

2. Site meteorological data taking into account distance and elevation for each of the 36 ten-degree sectors around the site, where estimated annual dose from PBAPS, if any, would be more

~

significant; 4

. .jp ~ -

,w. -, -+ a - n

l

3. On hills free from local obstructions and within sight of the vents I (where practical);

4. Near the dwelling closest to the main stack in the prevailing down wind direction.

A TLD set was placed at each location in a locked formica " birdhouse" or polyethylene jar located approximately six feet above ground level. The TLD ,

sets were exchanged monthly and quarterly, then sent to the laboratory for l analysis.

B. Data Interpretation  ;

Several factors are important in the interpretation of the data. These factors are discussed here to avoid undue repetition in the discussion of the results.

1. Minimum Detectable Level and Minimum Detectable Activity 1

The minimum detectable level (MDL) was defined as the smallest concentration of radioactive materialin a sample that would yield a net count (above background) that would be detected with only a 5%

probability of falsely concluding that a blank observation represents a "real" signal. The MDL was intended as a before the fact estimate of a system (including instrumentation, procedure and sample type) and not as an after the fact criteria for the presence of activity. All analyses were designed to achieve the required PBAPS detection capabilities for environmental sample analysis.

The minimum detectable activity (MDA) is defined above with the exception that the measurement is an after the fact estimate of the presence of activity.

2. Net Activity Calculation and Reportino of Results Net activity for a sample was calculated by subtracting background activity from the sample activity. Since the REMP measures extremely small changes in radioactivity in the environment, background variations will rer. ult in sample activity being lower than the background activity '

effecting a negative number. For a more detailed description of the results calculation, see Appendix E.  ;

1 Data reported in this report were generated using the convention of rounding the result to the same number of significant places as the first 1

significant digit in the error term (i.e., 3.62 i 1.23 rounds to 4 i 1; 10.93 i 0.96 rounds to 10.9 i 1.0; -0.01 0.1 rounds to 0.0 i 0.1). Results for each type of sample were grouped according to the analyses performed. For gamma analyses, at least those nuclides required for each sample media and nuclides which had a significant positive i occurrence were reported. Means and standard deviations of these results were calculated. These standard deviations represent the l variability of measured results for different samples rather than single i analysis uncertainty. l C. Program Exceptions, For 1995 the PBAPS REMP had a sample collection recovery rate of better than 99%. The exceptions to this program are listed below:

1. Air particulate and air iodine samples from location 1B were not available for week 36.(09/01/95 - 09/08/95) due to a combination electrical and mechanical problems. '

2. Surface water sampler at location 1MM was out of service for the following dates: 03/08/95 to 03/20/95,10/26/95 to 10/27/95, and 12/13/95 to 01/03/96 due to pump electrical, flow or weather problems.

Daily grab samples were taken.

~ 3. Surface water sampler at location 1LL was out of service for the following dates: 12/21/95 to 01/03/96 due to weather problems. Daily grab samples were taken.

4. The fourth quarter TLD from location 19 was found on the ground and its holder destroyed by vandalism. The TLD was not read.

5. Milk farm N went out of business beginning with the October 9,1995 '

sampling. Farm G was substituted for the QC program.

Each program exception was reviewed to understand the causes of the program exception. Sampling and maintenance errors were reviewed with the personnel involved to prevent a recurrence. Occasional equipment breakdowns and power outages were unavoidable. The overall sample recovery rate indicates that the appropriate procedures and equipment are in place to assure reliable program implementation.

D. Program Changes The following are the changes for the 1995 PBAPS REMP:

1

1. GPU Nuclear became the Primary Analytical Contract Laboratory, replacing Teledyne Brown Engineering (TBE). TBE replaced PSE&G as l the QC Laboratory.

l

2. Surface Water:

! Gross beta analyses were discontinued on all samples.

3. Drinking Water:

lodino-131 analysis was discontinued.

4. Air Particulate and Air lodine:

l The sampling program was reduced from seventeen locations to five locations. The Limerick Generating Station air particulate and air iodine station (22G1) was added to the REMP as a control location.

5. TLD:

The program was changed from forty-seven TLD locations to forty. The 1 l monthly frequency was discontinued. The quarterly sampling frequency l was maintained.

l l

l l

.g.

i I

} IV. Results and Discussion j A. Aquatic Environment i 1. Surface Water l

! Samples were collected from two locations monthly (1LL and 1MM). i

1LL served as the control location. The following analyses were j

performed. '

Tritium Samples from both locations were analyzed for concentrations of tritium j (Table C-l.1, Apper; dix C). Results ranged from 70 to 140 pCl/1 and

averaged 100 pCi/l at each location. The concentrations found were l

{ lower than those observed during the preoperational period. ,

t

. Gamma Soectrometry l

l Samples from both locations were analyzed for concentrations of ,

gamma emitters.(Table C-l.2, Appendix C). Statistically significant i activity for naturally occurring K-40 was found in 1 of 24 samples.  :

Potassium-40 results ranged from -3 to 35 pCl/l. No statistically '

significant fission or activation products were found.

2. Drinkina (Potable) Water Samples were collected from two locations monthly (4L and 61). 61 served as the controllocation. The following analyses were performed.

Gross Beta Samples from both locations were analyzed for concentrations of gross beta activity in insoluble and soluble fractions (Tables C-II.1 and C-II.2 and Figures C-1 and C-2, Appendix C). Gross beta activity in the insoluble fraction ranged from -0.9 to 1.4 pCi/1. The values in the soluble fraction ranged from 1 to 4 pCl/1. No differences were observed between the means of the control and indicator stations. The values were generally below those seen in the preoperational period.

Tritium Samples from both locations were analyzed for tritium concentration quarterly (Table C-II.3, Appendix C). The values for the indicator i

i f location (4L) ranged from 60 to 150 pCi/1 with a mean of 100 pCi/1.

L Control location (61) values ranged from -10 to 170 pCi/1 with a mean l of 60 pCi/1.: The concentrations found were lower than those observed during the preoperational period.

l Gamma Spectrometry

)

Samples from both locations were analyzed, for concentrations of gamma emitters (Table C-II.4, Appendix C). No statistically significant i activity was found for all nuclides searched for. )

i

3. Fish l

l Samples were collected from two locations semi-annually (4 and 6).

l The control location was 6. The following analyses were performed.

Gamma Soectrometry i

Statistically significant activity was observed only for the nuclide K-40 l which ranged from 2400 to 4000 pCi/kg (wet) (Table C-Ill.1, Appendix C). No statistically significant fission or activation products were found.

Figu's C-3 illustrates the Cs-137 activity for indicator and control locations from the beginning of the operational period through the i l present.

4. Sediment f

Samples were collected from three locations semi-annually (4J,4T and 6F). The control location was 6F. The following analyses were performed.

Gamma Soectrometry Samples from all locations were analyzed for concentrations of gamma j emitters (Table C-IV.1, Appendix C). Statistically significant activity for  ;

Be-7, K-40, Ra-226 and Th-228 was found at alllocations. K-40 results  ;

ranged from 12,000 to 22,000 pCi/kg (dry).

Statistically significant activity for the Plant produced nuclides Co-60  ;

were found in both samples from the indicator location 4J located downstream of the discharge. The results ranged from 0 to 40 pCl/kg

(dry) for the indicator locations and 2 to 10 pCi/kg (dry) for the control

! location. Statistically significant activity from Cs-137 was found at all j locations with a mean value of 230 pCi/kg (dry) for the indicator l - 11. -

l

~

locations and 200 pCi/kg (dry) for the control location. The calculated dose from this pathway to a teenager's skin was 1.37 E-03 mrem /yr.

This value is based upon the assumption the maximum concentrations of Co-60 and Cs-137 at the downstream location (4J) were present the

. entire year. This dose represents less than 0.01% of the allowable j fraction of 10 CFR 50, Appendix I limits. The results were consistent with those from previous years. Figure C-4, Appendix C illustrates the comparison of activities of Cs-137 detected at the control location and i indicator locations from the preoperational period through the present.

l B. Atmospheric Environment

1. Airborne l

l a. Air Particulates  !

L j j

Samples were collected from five locations (18,12, 2, 3A, and ,

l 22G1). Controllocation was 22G1. The following analyses were  !

performed.

Gross Beta Samples from all locations were analyzed for concentrations of gross beta (Tables C-V.1 and C-V.2 and Figures C-5 and C-6, Appendix C). Air particulate locations were divided into three groups: Group I, consisting of 1B,1Z, and 2, located on site at PBAPS; Group 11, comprised of 3A, located at an intermediate  ;

distance from PBAPS; and Group lil, consisting of 22G1, located at a remote distance from PBAPS. Comparison of results among  ;

these three groups aids in determining the effects, if any, resulting i from the operation 'of PBAPS. The results from site location l samples ranged from 4 to 30 E-3 pCi/m*, with a mean of 17 E-3 l pCi/m'. The results from intermediate distance location ranged i from 5 to 27 E-3 pCi/m', with a mean of 16 E-3 pCl/m'. The results i from the distant location ranged from 5 to 24 E-3 pCl/m*, with a mean of 15 E-3 pCl/m'. Comparison of the values indicate no notable difference among the three groups suggesting no effects from operation of PBAPS (Figure C-5, Appendix C).

l Gamma Spectrometry Weekly samples from five locatione (10 1Z,2. 3A, and 22G1) were I

, compcsited and analyzed quaderly for the pesence of gamma j emitters (Table C-V.3). Naturally occurring Be-7 was found in all  ;

i f l

l samples with activity values similar to those from the preoperational years. No statistically significant activation or fission products were detected.

i

, b.' Airborne lodine ,

I Continuous air samples were collected weekly at five locations (18, 12, 2, 3A, and 22G1) and analyzed for 1-131 (Table C-VI.1, Appendix C). No statistically significant I-131 was found.  ;

2. Terrestrial ,

a. Milk Samples were collected from eleven locations (A, B, C, D, E, G, J,

! L, N,0 and P). Farms A, B, C, and E were control locations. The  :

! following analyses were performed.

lodine-131 Samples from all locations were analyzed for concentrations of I-131 (Tables C-Vil.1, Appendix C). All results were less than the minimum detectable level and ranged from -0.3 to 0.2 pCi/l.

I Gamma Soectrometry Samples from five locations were analyzed quarterly for concentrations for gamma emitters (Table C-Vil.2 and Figure C-7, Appendix C). Naturally occurring K-40 was found in all samples with values ranging from 1,300 to 1,500 pCi/l. All other nuclides searched for were less than the minimum detectable activity.

C. Ambient Gamma Radiation Ambient gamma radiation levels were measured quarterly at forty locations (as described in the program description section) using Panasonic 801 (CaSO4) thermoluminescent dosimeters (Tables C-Vill.1 through C-Vill.3 and Figures C-8 and C-9, Appendix C). All TLD readings were below 10 mR/std. ,

month with a range of 3.3 to 7.0 mR/std. month.

i' 1

s V. References j

, 1. Preoperational Environs Radioactivity Survey Summary Report, March,1960 through January,1966. (September 1967). ,

l

2. Interex Corporation, Peach Bottom Atomic Power Station Regional Environs Radiation Monitoring Program Preoperational Summary Report, Units 2 and 3, 5 February 1966 through 8 August 1973, June 1977, Natick, Massachusetts.

I

! 3. Radiation Management Corporation Publication, Peach Bottom Atomic Power Station Preoperational Radiological Monitoring Report for Unit 2 and 3, January,1974, Philadelphia, Pennsylvania.

l 3

4 i

i i

t l I

i.

l 6

I

1 1

4 4 i l

) '

l

.i 4 1

1 l

APPENDIX A ,

1 i

l l

RADIOLOGICAL ENVIRONMENTAL MONITORING REPORT

SUMMARY

l l

1 2

_ - . - _ _ _ _ _ _ . _ _ . _ _ _ _ _ _ _ _ _ _ _ - _ - . _ - _ - _ - _ _ - - - _ _ - - - - - _ - - _ _ - _ - _ _ _ _ _ _ . _ - _ - _ _ - - _ - _ _ _ _ - - _ _ - - . _ . _ _ _ _ _ - - - . _ _ _ _ _ _ _ _ _ _ _ _ _ _ - - - _ _ _ _ _ _ _ _ _ - - _ - . _ _ _ _ _ - _ - . ~ . _ _ - - _ _ _ _ _

APPENDIX A RADIOIDGICAL ENVIROtGEENTAL MONITORING PROGRAM ABNUAL SUBetARY IEADIE OF FACILITY: PEACE BOTTON ATOttIC POWER FFATION DOCKET NO. 50-277 & 50-2?8 LOCATIOtt OF FACILITY: YORK COUNTY, PA REPORTIK*3 PERIOD: 1995 INDICATOR CONTROL LOCATION WITE RIGERST REQUIRED IACATIONS LOCATIONS ANNUAL BEEAN IfUBEBER MEDIUlf OR TYPE OF NUMBER OF MINIMUBt MEAbt BERAN BERAN STATION 9 OF af0NROUTINE PATENAY SAMPLED ANALYSES ANALYSES DETECTABLE (F) (F) (F) NABER RCPORTED (UNIT OF BERASUREMENT) PERFORIEED PERFORDEED LEVEL (MDL) RAROGE RANGE RAIOGE DISTARICE t. DIRECTIOtt NBASUF2BEElfr8 SURFACE NATER TRITIUM 8 1200 100 100 100 last (INDICATOR' O (PCI/ LITER) (4/4) (4/4) (4/4) CANAL DISCRARGB .

(70/140) (70/120) (70/140) 1.04 MILES SE OF Sart GAISEE 24 R-40 N/A 18 15 18 ilet (INDICATOR) 0 (12/12) (12/12) (12/12) CANAL DISCRARGE

(-3/35) (-3/25) (-3/35) 1.04 MILES SE OF SITE ser-54 9 -0.2 -0.1 -0.1 ILL (CotrTROL) 0.

(12/12) (12/12) (12/12) UNITS 2 & 3 IllTAKE

(.1.4/0.8) (-1.1/0.6) (-1.1/0.6) 0.24 MILES BRIE OF SITE CO-58 9 -0.5 -0.3 -0.1 1LL (CollTROL) 0 (12/12) (12/12) (12/12) Ulf1TS 2 & 3 INTAKE

(-1.6/0.2) (.1.4/0.9) (.1.4/0.9) 0.24 MILES IIII OF SITE FE-59 18 1 0 1 1 set (INDICATOR) 0 (12/12) (12/12) (12/12) CAREAL DISCRARGE

(-1/4) (-2/2) (-1/4) 1.04 MILES SE OF SITE CO.60 9 0.1 -0.1 -0.1 1LL (CobrfROL) 0 (12/12) (12/12) (12/12) UNITS 2 & 3 IIITARE

(-0.8/0.4) (-0.5/0.8) (-0.5/0.8) 0.24 MILES ElfE OF SITE EN-65 18 -4 -3 3 1LL (COllTROL) 0 (12/12) (12/12) (12/12) UNITS 2 & 3 INTAKE

(-9/0) (-7/3) (-7/3) 0.24 MILES ElfE OF SITE ER-95 9 0 0 0 1998 (INDICATOR) 0 (12/12) (12/12) (12/12) CANAL DISCRARGE

( 1/1) (-2/1) (-1/1) 1.04 MILES SE OF SITE NB-95 9 0.4 0.4 0.4 ILL (CotETROL) 0  ;

(12/12) (12/12) (12/12) UNITS 2 & 3 INTARE 6

(-2.2/3.1) (-0.5/1.8) (-0.5/1.8) 0.24 MILES ElfE OF SITE

- l i

FRACTIOtt OF DETECTABLE IERASUREBERSITS AT SPECIFIED I4 CATIONS IS INDICATED IN FARElffEESES (F).

A .1

_ = _ _ _ _ _ _ _ _ _ _ _ _ _ - _ - _ _ - _ _ _ _ _ _ _ - _ _ _ - - - _ _ _ _ _ _ - _ _ _ _ _ _ - _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ - - _ _ _ _ _ _ _ _ _ _ _ - _ _ _ - _ - _ _ _ _ - _ - _ _ - _ _ _ - - _ _ _ _

m, I

r APPENDIX A RADIOLOGICAL ENVIROISEENTAL MONITORING PROGRAN ANNUAL SUBSEARY ,

NAME OF FACILITY: PEACII BOTTott ATONIC POWER STATION DOCKET Iso.: 50-277 a 50-278 14 CATION OF FACILITY: YORK COUNTY, PA REPORTING PERIOD: 1995 INDICATOR COtrFROL IACATION WITE RIGBEST REQUIRED LOCATIONS LOCATIONS AIREUAL MEAN NUMBER MEDIUM OR TYPE OF NUDEBER OF MINIMUM MEAN MEAII MEAN STATION 9 OF NONROUTISEE PATHWAY SABEPLED AttALYSES AttALYSES DETECTABLE (F) (F) (F) BEAME REPORTED (UNIT OF MEASUREMEllT) PERFORMED PERFOIWEED LEVEL (BEDL) RAIOGE RAleGE RANGE DISTANCE a DIRECTION BERASUREBEEtrFS CS-134 9 -1.7 -1.7 -1.7 1LL (COtrFROL) 0 (12/12) (12/12) (12/12) UNITS 2 a 3 IllTAKE

(-7.3/0.5) (-6.7/0.9) (-6.7/0.9) 0.24 MILES ENE OF SITE i CS-137 11 -0.3 0.0 0.0 1LL (CONTROL) 0 (12/12) (12/12) (12/12) UltITS 2 a 3 INTAKE

(-1.7/0.41 (-0.6/1.3) (-0.6/1.3) 0.24 MILES ElfE OF SITE BA-140 9 -1 -1 -1 13st (IllDICATOR) 0 (12/12) (12/12) (12/12) CAREAL DISCRARGE

(-5/2) (-4/5) (-5/2) 1.04 MILES SE OF SITE ,

LA-140 9 1 0.1 0.1 1LL (COtf?ROL) 0 (12/12) (12/12) (12/12) UtIITS 2 a 3 ItrFAKE

(-5/2) (-1.0/0.9) (-1.0/0.9) 0.24 IIILES EIEE OF SITE DRINKIIIG WATER GROSS BETA 24 2.5 2.2 2.4 2.4 6I (COblTROL) 0 (PCI/ LITER) SOLUBLE (12/12) (12/12) (12/12) ROLTWOOD STATION INTAKE (1.0/4.2) (0.8/4.5) (0.8/4.5) 5.74 MILES IfW OF SITE GitOSS BETA 24 2.5 0.2 0.3 0.3 61 (CONTROL) 0 f INSOLUBLE (12/12) (12/12) (12/12) BOLTWOOD STATIOtt INTAKE i

(-0.9/1.4) (.0.7/1.2) (-0.7/1.2) 5.74 MILES RfW OF SITE ,

TRITIUtt 8 1200 100 60 100 SL (INDICATOR) 0 (4/4) (4/4) (4/4) cot 00WIROGO DAM EL 33FT. COMPOS (60/150) (-10/170) (60/150) 8.66 MILES SE OF SITE GA8 SEA 24 R.40 N/A 17 12 17 4L (INDICATOR) 0 (12/12) (12/12) (12/12) COGIOWINGO DAN EL 33FT. CottPOS

(-20/38) (-6/31) (-20/38) 8.66 MILES SE OF SITE 188-54 9 -0.2 0.3 -0.2 4L (INDICATOR) 0 (12/12) (12/12) (12/12) COIGOWINGO DAM EL 33FT. CottPOS

(-0.7/0.3) (-2.2/0.5) (-0.7/0.3) 8.66 MILES SE OF BITE I

FRACTIOff OF DETECTABLE SERASUREBEEtrFS AT SPECIFIED LOCATIOtBS IS IREDICATED IN PARElfTRESES (F).

A-2

APPENDIX A RADIOLOGICAL ENVIRotSEENTAL MONITORING PROGRAM AsafUAL SUtetARY MADER OF FACILITY PEACR BOTTott ATOMIC POWER STATION DOCKET NO. 50-277 & 50-274 LOCATION OF FACILITY: YORK COUNTY, PA REPORTING PERIOD: 1995 INDICATOR CONTROL LOCATION WITE HIOREST REQUIRED LOCATIONS LOCATIONS ARESUAL MEAN NUMBER MEDIUlf OR TYPE OF NUBEEER OF MINIMUlf DERAN MEAN MEAN STATIOtt 9 OF NONROUTINE PAT 9ntAY SAMPLED ANALYSES ANALYSES DETECTABLE (F) (F) (F) NAME REPORTED (UNIT OF MEASUREBEENT) PERFOttMED PERFoltBEED LEVEL (MDL) RARIGE RANGE RANGE DISTANCE & DIRECTION MEASUREMENTS

.-------=_. - _ - ---------... ......--- -----....--. --.........- ------------- ----- ----------------------------. ------------.

CO-58 9 -0.1 -0.1 -0.1 4L (INDICATOR) 0 (12/12) (12/12) (12/12) cot 00WINGO DAIE EL 33FT. C00EPOS

(-0.9/0.7) (-0.7/0.7) (-0.9/0.7) 8.66 MILES SE OF SITE FR-59 18 0 0 0 6I (CONTROL) 0 (12/12) (12/12) (12/12) EOLTWOOD STATIOtt INTAKE

(-1/3) (-2/2) (-2/2) 5.74 MILES WW OF SITE CO-60 9 0.1 0.3 0.3 61 (CONTROL) 0 (12/12) (12/12) (12/12) BOLTWOOD STATIOtt INTAKE

(-2.0/1.5) (.1.0/2.3) (-1.0/2.3) 5.74 MILES BfW OF SITE EW-65 18 -3 -2 -2 6I (CONTROL) 0 (12/12) (12/12) (12/12) NOLTWOOD STATIOtt INTAKE i

(-5/2) (-6/1) (-6/1) 5.74 MILES NW OF SITE ER-95 9 0 1 1 6I (ColeTROL) 0 (12/12) (12/12) (12/12) EOLTWOOD STATIOtt IIITARE (0/1) (-1/3) (.1/3) 5.74 MILES IIIt OF SITE NE-95 9 0.4 0.5 0.5 EI (COtf?ROL) 0 (12/12) (12/12) (12/12) MOLTWOOD STATIOtt INTAKE

(-1.3/3.9) (-0.5/2.2) (-0.5/2.2) 5.74 MILES BfW OF SITE CS-134 9 2.0 -1.7 -1.7 6I (CORITROL) 0 (12/12) (12/12) (12/12) NOLTWOOD STATIOtt INTAKE

(-8.8/0.5) (-7.0/1.4) (-7.0/1.4) 5.74 MILES IEW OF SITE CS-137 11 0.0 -0.1 0.0 4L (INDICATOR) 0 (12/12) (12/12) (12/12) cot 00NIIOGO DAM EL 33FT. CottPOS

(-0.4/1.0) (-0.7/0.7) (-0.4/1.0) 8.66 MILES SE OF SITE BA-140 9 1 1 1 6I (CONTROL) 0 (12/12) (12/12) (12/12) EOLTWOOD STATION INTARE

(-4/4) (-2/3) (-2/3) 5.74 MILES 10W OF SITE LA-140 9 0.1 0.1 0.1 6I (CONTROL) 0 (72/12) (12/12) (12/12) ROLTWOOD STATIOtt INTARE

(.1.2/1.9) (-1.2/1.0) (-1.2/1.0) 5.74 DEILES REW OF SITE FRACTIOtt OF DETECTABLE SERASUREMB9fTS AT SPECIFIED LOCATIOtts IS INDICATED IN PARENTHESES (F).

A-3

APPENDIX A RADIOLOGICAL ENVIROISSENTAL MONITORING PROGRAM ANNUAL SURGIARY NAbtB OF FACILITY: PEACE BOTTON ATOMIC POWER STATION DOCRET NO. 50-277 & 50-278 LOCATION OF FACILITY: YORK COUNTY, PA REPORTING PERIOD: 1995 INDICATOR CONTROL LOCATIOtt WITE HIGBBST REQUIRED LOCATIONS LOCATIONS ANNUAL MEAN NUDEBER MEDIUM OR TYPE OF NUMBER OF MINIMUM MEAN MEAN MEAN STATION 9 OF NOIEROUTINE PATNWAY S?JtPLED ANALYSES ANALYSES DETECTABLE (F) (F) (F) NAME REPORTED (UNIT OF BRASUREMENT) PERFORIEED PERFORMED LEVEL (MDL) RANGE RANGE RANGE DISTANCE & DIRECTIOtt MEASUREMENTS

. . - - . . . - . . . . . . - - . . . . . - . . - . . . . . . . . . . . . . . . - - . . . . . . . . . . - - - - - - - - . - - - - - . . . . . - - - - - - - - - . . - - - - - - - - - . - - = . _ - - - = - - - ....--........ ....--...--..

PREDATOR (FISH) GAIStA 4 (PCI/RG WET) K-40 N/A 3700 3500 3700 4 (INDICATOR) 0 (2/2) (2/2) (2/2) CONOWINGO POttD bet 4W DISCRARG (3300/4000) (3400/3600) (3300/4000) CONOWIBOGO POND - BE!4W DISCRA Mit-54 SO O 1 1 6 (CONTROL) 0 (2/2) (2/2) (2/2) NOLTWOOD POIED

(-2/2) (-1/3) (-1/3) ROLTWOOD POND CO-58 80 -1 1 -1 6 (COtfTROL) 0 (2/2) (2/2) (2/2) NOLTWOOD PotID

(-3/0) (-3/0) (.3/0) NOLTWOOD PolfD FE-59 160 -1 0 0 6 (CONTROL) 0 (2/2) (2/2) (2/2) BOLTWOOD PODED  !

(-3/2) (0/10) (0/10) HOLTWOOD PottD  !

Co-60 80 1 4 4 6 (COtFFROL) 0 (2/2) (2/2) (2/2) NOLTWOOD PotID (0/2) (2/7) (2/7) ROLTWOOD POttD i RN-65 160 -10 -30 -10 4 (INDICATOR) 0 (2/2) (2/2) (2/2) cot 00WINGO POffD BELOW DISCRARG

(-20/0) (-30/-20) (-20/0) CONOWIIGOO POND - BELOW DISCHA Cs-134 90 -5 2 2 6 (COff?ROL) 0 (2/2) (2/2) (2/2) ROLTWOOD PotfD

(-10/0) (2/2) (2/2) BOLTWOOD POIED Cs-137 90 3 0 3 4 (IREDICATOR) 0 (2/2) (2/2) (2/2) cot 00WIIIGO POND BELOW DISCHARG (3/3) (-4/4) (3/3) CONOWIIIGO PottD - BELOW DISCRA BOTTODE FEEDER (FISII) GAIStA 4 (PCI/RQ WET) K-40 N/A 2000 2700 2000 4 (INDICATOR) 0 (2/2) (2/2) (2/2) cot 00WIIIGO PotED bet 4W DISCHARG (2500/3100) (2400/2900) (2500/3100) cot 00WIROGO POND - BELOW DISCRA i

. t FRACTIOlt OF DETECTABLE MEASUREBEENTS AT SPECIFIED 14CATIOtts Is INDICATED IN PARENTHESES (F).

A-4 >

APPENDIX A RADIOLOGICAL ENVIROISERNTAL MONITORING PROGRAN ANNUAL SUBSEARY NABER OF FACILITY: PEACE BOTTOBE ATOBEIC POWER STATION DOCKET NO.: 53-277 & 50-278 IDCATIOtt OF FACILITY: YORK COUllTY, PA l REPORTING PERIOD: 1995  ;

I% OTOR CONTROL LOCATIOtt WITE RIGEEEST REQUIRED LOCATIDIOS LOCATIOttS ABINUAL BERAN NUtaER DEEDIUlf OR TYPE OF IEUBEBER OF MINIMUtt BEEAlt BERAN MEAN STATIOtt S PATHWAY SABEPLED ANALYSES OF IIONROUTIllE AllALYSBS DETECTABLE (F) (F) (F) BEADER REPORTED I (UNIT OF NBASUREBEENT) PERFolt9EED PERFORIEED LEVRL (MDL) RAIIGE RANGE RANGE DISTANCE & DIRECTIOtt

. . . . . . . . . . . . . . . . . _ _ _ . . . . . . . - - - NBASURENEIFFS

__= ..____... ............ -_ _ - - - - _ _ ............. .==---- _ _ . _ _ . . . . _ . . . . . . = = = - __ -

= ... =-

3e8-54 80 1 -1 1 4 (INDICATOR) 0 (2/2) (2/2) (2/2) ColeOWIIIGO POIED BRI4W DISCEARG (0/1) (-3/1) (0/1) COBOOWIIIGO POIID - BELOW DISCEA '

CO-50 80 4 0 0 6 (CoelTitOL) 0 .

(2/2) (2/2) (2/2) ROLTWOOD POND '

(-4/-3) (0/0) (0/0) BOLTWOOD PORED FE-59 160 10 0 10 4 (IIEDICATOR) 0 (2/2) (2/2) (2/2) cot 00WINGO POND bet 4W DISCEARG (0/10) (0/10) (0/10) CotsOWINGO POtID - BELOtt DISCHA

. CO-60 80 1 0 0 6 (CotrTROL) 0 (2/2) (2/2) (2/2) NOLTWOOD POND

(-1/-1) (-1/0) (-1/0) ROLTWOOD POIID q.

7 SM-65 160 0 -10 0 4 (INDICATOR) 0 '

(2/2) (2/2) (2/2) ColeOWIIIGO PdND BELOW DISCEARG

(-10/0) (-20/-10) (-10/0) COtIOWileGO POIED - BELOW DISCHA CS-134 90 4 -18 4 4 (INDICATOR) 0 (2/2) (2/2) (2/2) Cot 00WINGO PotED BELOW DISCIIARG i (3/4) (-21/-15) (3/4) COEIOWIl0GO PotID - BRIDIt DISCHA CS-137 90 2 6 6 6 (ColeTROL) 0 (2/2) (2/2) (2/2) NOLTWOOD POtID (1/3) (4/8) (t/8) HOLTWOOD POIID EILT GABSth 6 (PCI/KG DRY) BB-7 N/A 210 170 400 4T (INDICATOR) O t (4/4) (2/2) (2/2) CONOWIleGO PotsD IIBAR CORIOWINGO

(-60/670) (-10/350) (200/700) 7.92 NILES SE OF SITE K-40 N/A 18000 13000 22000 4T (INDICATOR) 0 (4/4) (2/2) (2/2) C0000WIIIGO POGED NEAR Cot 00WIIOGO (12000/22000) (11000/14000) (21000/22000) 7.92 NILES SE OF SITE t

FRACTION OF DETECTABLE SERASUREBEENTS AT SPECIFIED LOCATIOEIS IS INDICATED IN PARERWTitBSES (F).

A-5

APPENDIX A RADIOLOGICAL ENVIRotetRNTAL MONITORING PROGRAM ANNUAL SUtetARY NAME OF FACILITTe PEACR BOTTOM ATOMIC POWER STATION DOCKET NO.e 50-277 & 50-278 IcCATION OF FACILITY: TORK COUNTY, PA REPORTING PERIODS 1995 INDICATCR CONTROL LOCATION WITE HIGEEST REQUIRED LOCATIONS LOCATIONS ANNUAL MEAN MEDIUM OR TYPE OF NUMBER OF MINIMUM MEAN NUMBER MEAN MEAN STATION 9 PATEWAY SAMPLED ANALYSES OF NONROUTINE ANALYSES DETECTABLE (F) (F) (F) NAME REPORTED (UNIT OF MEASUREMENT) PERFORMED PERFOIGEED LEVEL (MDL) RANGE RANGE RANGE DISTANCE & DIRECTION

..................... = --=--- _- =. ......... ............ ......-. . . . . . . . . . . . . . . . = - _ -

MEASUREMENTS CO-60 N/A 20 4 30 4J (INDICATOR) 0 (4/4) (2/2) (2/2) CONOWINGO POND NET TRAP 15 (0/40) (2/6) (20/40) 1.39 MILES SE OF SITE CS-134 100 6 5 6 4J (INDICATOR) 0 (4/4) (2/2) (2/2) CONOWINGO POND NET TRAP 15 (3/10) (5/5) (3/10) 1.39 MILES SE OF SITE CS-137 100 230 200 230 4J (INDICATOR) 0 (4/4) (2/2) (2/2) CONOWINGO POND NET TRAP 15 (100/360) (100/310) (100/360) 1.39 MILES SE OF SITE RA-226 N/A 2200 2700 2700 6F (CONTROL) 0 (4/4) (2/2) (2/2) EOLTNOOD DAM EAST SEORE UPSTR (1300/2600) (2100/32005 (2100/3200) 5.96 MILES IW OF SITE 75-232 N/A 1200 1240 1500 4T (INDICATOR) 0 (4/4) (2/2) (2/2) CONOWINGO POND NEAR CONOWINGO (680/1500) (870/1600) (1400/1500) 7.92 MILES SE OF SITE AIR PARTICULATE GROSS BETA 259 6 17 15 17 1B (INDICATOR) 0

(:1-3 PCI/CU. METERI (207/207) (52/52) (51/51) WEATERR STATION NO.2 (4/30) (5/24) (4/30) 0.49 MILES NW OF BITE GApetA 20 33-7 N/A 70 70 80 2 (INDICATOR) 0 (16/16) (4/4) (4/4) SITE, 130 DEGREE SECTOR EILL (40/110) (50/90) (70/110) 0.89 MILES SE OF SITE K-40 N/A 5 10 10 2201 (CONTROL) 0 (16/16) (4/4) (4/4) MANOR SUBSTATION

(-11/21) (10/20) (10/20) 30.79 MILES NE OF SITE CS-134 40 -0.2 -0.4 0.2 11 (INDICATOR) 0 (16/16) (4/4) (4/4) WEATHER STATION 1

(-3.1/0.9) (-0.7/-0.1) (-0.8/0.9) 0.26 MILES SE OF SITE FRACTIOtt OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARBirrHESES (F).

A-6

. ~ . . ~ _ . - . . - -. .. .-- .

APPENDIX A RADIO 1DGICAL ENVIROlGERNTAL MOttITORING PROGRAM ANNUAL SUBStARY NAME OF FACILITY: PEACE BOTTOM ATOMIC POWER STATION DOCKET NO. 50-277 & 50-278 LOCATIOtt OF FACILITY: TORK COU!PfT, PA REPORTING PERIOD: 1995 INDICATOR CONTROL LOCATION WITH RIGREST REQUIRED EDCATIONS 1ACATIOt88 AMitDAL MEAN NUMBER MEDIUM OR TYPE OF NUBEBER OF MINIMUM MEAN MEAN MEAN STATION 5 OF tsOefROUTINE PAT 11WAY SAMPLED ANALYSES AltkLYSBS DETECTABLE (F) (F) (F) NAME REPORTED (UltIT CF 9tEASUREMENT) PERFORATED PERFOIGGED LEVEL (MDL) RANGE RANGE RANGE DISTANCE & DIRECTIOtt MEASUREMEffTS CS-137 40 -0.3 0.1 0.1 22G1 (COtFFROL) 0 (16/16) (4/4) (4/4) MAleOR SUBSTATION

(_1.2/0.6) (-0.5/0.7) (-0.5/0.7) 30.79 MILES ISE OF SITE RA-226 N/A 10 20 20 22G1 (CONTROL) 0 (16/16) (4/4) (4/4) MAISOR SUBSTATION

(-20/30) (10/30) (10/30) 30.79 MILES NE OF SITE TE-232 N/A 0 C 1 15 (INDICATOR) 0 (16/16) (4/4) ( 4 '4 ) WEATHER STATIOtt 1

(-2/3) (-3/2) (- J/3) 0.26 MILES SE OF SITE A13 IODINE I.131 259 40 0 0 1 11 (INDICATOR) 0 (C-3 FCI/CU. METER) (207/207) (52/52) (52/52) WEATNER STATION 1

(.21/23) (-11/15) (-11/21) 0.26 MILES SE OF BITE MILK I-131 124 0.6 0.0 0.0 0.1 P (INDICATOR) 0 (PCI/ LITER) (91/91) (33/33) (4/4) INTERptEDIATE DISTANCE FAIGE P

(-0.3/0.3) (-0.2/0.2) (0.0/0.2) 2.08 MILES ENE GF SITE GMeth 19 R-40 N/A 1400 1400 1400 O (INDICATOR) 0 (15/15) (4/4) (4/4) NEkRBY FARM G (1300/1500) (1300/1400) (1300/1500) 1.49 MILES SSW OF SITE CS-134 10 -3.6 -3.3 -3 O (INDICATOR) 0 (15/15) (4/4) (4/4) IfEARBY FARM O

(-8.3/0.8) (-5.2/1.0) (-8/1) 2.32 MILES SW OF SITE CS-137 10 0.3 0.5 1.0 J (INDICATOR) 0 (15/15) (4/4) (4/4) NEARBY FARM J

(-1.2/1.8) (-0.3/1.8) (0.2/1.8) 0.97 MILES W OF SITE BA-140 9 -1 3 3 A (COffTROL) 0 (15/15) (4/4) (4/4) DISTANCE FARM A

(-4/3) (0/5) (0/5) 5.78 MILES WSW OF SITE FRACTIOtt OF DETECTABLE HEASUREDIESPFS AT SPECIFIED LOCATIOtts IS INDICATED IN PARENTHESES (F).

A-7

- .-. . ~ _ . . , - . . -. . . . . . - - . _- . . . _ . - _. .- _

APPENDIX A RADIOLOGICAL EN7IROSSIENTAL MONITORING PROGRAtt ANNUAL SUtstARY MANE OF FACILITY: PEACH EOTTOtt ATOttIC POWER STATIOtt DOCKET NO.: 50-277 & 50-278 14CATIOtt OF FACILITYe YORR COUNTY, PA REPORTING PERIOD: 1995 INDICATOR CottTROL IDCATIOtt WITE NIOREST REQUIRED LOCATIOtts LOCATIotes ANNUAL MEAN NUMBER NEDIUti OR TYPE OF NUttBER OF MININ098 MEAN MEAN MEAN STATIOtt # OF NottROUTINE PATHWAY SAlfPLED ANALYSBS AllALYSES DETECTABLE (F) (F) (F) NAME REPORTED (UNIT OF MEASUREttENT) PERFOISIED PERFORMED LEVEL (BIDL) RAltGE RANGE RANGE DISTANCE & DIRECTIOtt NEASUREMENTS

. . . . . . . . . . . . . . . . . - - . . = = - - = = = = - - - --

-== ...--------- --..-.....--- --...... -. - ......------- ........--..... ---------... ...----..----

LA.140 9 0.2 1.0 1 O (INDICATOR) 0 (15/15) (4/4) (4/4) IIBAREY FAmat O

(-1.8/1.8) . (0.1/2.3) (0/2) 2.32 MILES SW OF SITE

[ DIRECT RADIATION TLD-QUARTERLY 159 N/A 5.32 5.26 6.65 50 (INDICATOR) 0 (MILLI-ROEttTOBat / (144/144) (15/15) (4/4) TRANSCO FUttPIltG STATIOtt STD. BIDIITE) (3.30 7,00) (4.00-6.00) (6.40-7.00) 4.99 NILES W OF SITE t

t FRACTIOtt OF DETECTABLE MEASURENEIFPS AT SPECIFIED 14CATIOtts IS INDICATED IN PABEWPHESES (F).

A-8

4 4

e 1

i 4

4 d

4 i

1 i

4 i,

1 4 s t,

t APPENDIX B i

5 i

! SAMPLE DESIGNATION h

AND LOCATIONS 1

I a

i

APPENDIX B: SAMPLE DESIGNATION AND LOCATIONS LIST OF TABLES AND FIGURES TABLES TABLE B-1: Sample Collection and Analysis Program for the Radiological Environmental Monitoring Program, Peach Bottom Atomic Powr Station,1995 FIGURES FIGURE B-1: Environmental Sampling Locations on Site or Near the Peach Bottom Atomic Power Station,1995 FIGURE B-2: Environmental Sampling Locations at Intermediate Distances from the Peach Bottom Atomic Power Station,1995 FIGURE B-3: Environmental Sampling Locations at Remote Distances from the Peach Bottom Atomic Power Station,1995 1

B-i t

~

TABLE B-1: Sample Collection and Analysis Program for the Radiological Environmental Monitoring Program for Peach Bottom Atomic Power Station,1995 Location Location Description Distance & Collection Method and Frequency Analysis & Frequency Direction from Performed--Consultant PBAPS Vents A. Surface Water 1LL Peach Bottom Units 2 0.24 miles NE Water is continuously collected in a 190 gallon Gamma Spec monthly - GPU and 3 Intake - tank. Each week 2 quarts are withdrawn from Tritium - quarterly - GPU Composite (Control) the tank prior to draining the tank and placed in a 2 gallon polyethylene bottle to form a monely corgoslie sample 1MM Peach Bottom Canal 1.04 miles SE Same as location 1LL Same as location ILL '

Discharge -Composite N B. Driniona (Potable) Water . , .

4L Conowingo Dam EL 8.66 miles SE Water is continuously sampled from a header Gross Beta (Sal) - monthly - GPU 33' MSL - Composite which draws pond water from elevation 33' Gamma Spec - monthly - GPU MSL and is collected in a 175 gallon tank. Tritium - quarterly - GPU Each week 2 quarts are withdrawn from the tank prior to draining the tank and placed in a Gross Beta (Sal)- monthly - TBE*

2 gnBon polyethylene bottle to form a monthly Gamma Spec - monthly - TBE*

composite sarmle.

61 Holtwood Dam - 5.75 rniles NW Water is continuously sampled from the Same as location 4L Hydroelectric Station - Holtwood Hydici;trlc Station Intake and is Composite (Control) collected in a 175 gallon tank. Each week 2 quarts are withdrawn from the tank and placed in a 2 gallon polyethene bottle to form a monbly cornposite.

B-1

TABLE B-1: Sample Collection and Analysis Program for the Rac50!ogical Environmental Monitoring Program for Peach Bottom Atomic Power Station,1995 Location Location Description Distance & Collection Method and Frequency Analysis & Frequency Direction from Performed--Consultant PBAPS Vents C. Fish 4 Conowingo Pond Located in Conowingo Fish from two groups represeneng predator Gamma Spec semiannually - GPU Pond below the and bottom feeder species collected by dscharge electrofishing or other fishery gear somlannually 6 Holtwood Pond Located in Holtwood Same as location 4 Same as location 4 (Control) Pond D. Sediment ,

4J Conowingo Pond near 1.39 miles SE Recently deposited sediment collected below Gamma Spec - somlannually - GPU Berkins Run the wateriine, semi-annually 4T Conowingo Pond near 7.92 miles SE Same as location 4D Same as location 4D Conowingo Dam 6F Holtwood Dam 5.96 miles NW Ssme as location 4D Same as location 4D 1 (Control) ,

E. Air Particulate - Air lodine 1B Weather Station #2 0.49 miles NW About 1 cfm contmuous flow through glass Gross beta -weekly GPU fiber and charcoal filters (approx. 2" dameter} Gamma Spec - quarterly - GPU which are installed for a week and replaced 1-131 - weekly - GPU 1Z Weatier Station #1 0.26 miles SE Same as location IB Same as location 18 1A Weather Staton #1 0.26 miles SE Same as location 1B Gross beta - weekly - TBE*

Garnma Spec - quarterfy - TBE*

B-2

TABLE B-1: Sample Collection and Analysis Program for the Radiological Environmental Monitoring Program for Peach Bottom Atomic Power Station,1995 Location Location Description Distance & Collection Method and Frequency Analysis & Frequency Direction from Performed--Consultant PBAPS Vents 2 On-site - 130* Sector 0.88 miles SE Same as location IB Same as location IB t till 3A Delta, PA - Substation 3.62 miles SW Same as location 1B Same as location 1B 22G1 Manor Substation 30.79 miles NE Same as location IB Same as location 1B F. Mik A (Control) 5.78 miles WSW Two gallon grab sanpie is collected at each I-131 - biweekly, monthly" - GPU farm from a bulk tank containing milk biweekly Gamma Spec - quarterfy - GPU while cows are on pasture, monthly other times 1-131 - quarterly - TBE*

Gamma Spec - quarterfy - TBE*

B (Control) 10.58 miles S Same as Farm A l-131 - quarterly - GPU C (Control) 9.54 miles NW Same as Farm A Same as Farm B D 3.51 miles NE Same as Farm A Same as Farm B E (Control) 8.74 miles N Same as Farm A Same as Farm B G 1.49 miles SSW Same as Farm A l-131 - biweekly, monthly ** - GPU Gamma Spec - quarterly - GPU J 0.97 miles W Same as Farm A Same as Farm A L 2.12 miles NE Same as Farm A Same as Farm B N 3.03 miles ESE Same as Farm A Same as Farm A O 2.32 rniles SW Same as Farm A Same as Farm B B-3

TABLE B-1: Sample Collection and Analysis Program for the Radiological Environmental Monitoring Program for Peach Bottom Atomic Power Station,1995 l

l Location Location Description Distance & Collection Method and Frequency Analysis & Frequency I Direction from Perfotmed--Consultant i PBAPS Vents i

P 2.08 muss ENE Same as Farm A Same as Farm B  !

I G. Envwonmental Dossnetry - TLD Site Boundary IL Peas Bonom Unit 3 0.24 mRes NE Collection method and frequency is described TLD - quarterly - GPU intake in placement proce&re Section Ill. A. - j 1A Weaher Staton #1 0.26 miles SE ,

y%.

2 Pead Bonom 130' O.88 miles SE $Iame as location 1L Sector Hil 11 Peas Bottom South 0.54 mRes SSE Same as location 1L Substadon 1C Poes Bottom South 0.85 miles SSE Same as locanon IL Substation 1J Peam Bottom 180* 0.71 miles S Same as location IL Sector HH i 1F Pead Bonom 200* 0.51 miles SSW Same as location 1L i Sector Hil 40 Pead Bottom Site 1.46 miles SW Same as location IL i Area l

1NN Pead Bottom Site 0.48 miles WSW Same as location IL 1H Pod Bottom 270* 0.59 miles W Same as location 1L Sector Hil i r

i i

B-4

TABLE B-1: . Sample Collection and Analysis Program for the Radiological Environmental Monitoring Program for Peach Bottom Atomic Power Station,1995 Location Location Description Distance & Collection Method and Frequency Analysis & Frequency Direction from Performed--Consultant PBAPS Vents 1G Peach Bonom North 0.60 miles WNW Same as locanon 1L Substation IB Westwr Staton #2 0.49 miles NW Same as locaelon 1L 1E Peach Bottom 350' O.59 miles NNW Same as location IL Sector Hil Intermodlate Distance 15 SRyer Spring Rd 3.68 miles N Same as locanon 1L 22 Eagle Road 2.39 miles NNE Same as location 1L 44 Goshen Mill Rd 5.07 miles NE Same as location IL 32 State Hlu Rd 2.75 miles ENE Same as location IL 45 PB-Koeney Line 3.38 miles ENE Same as locanon IL 14 Peters Creek 1.97 miles ESE Same as location 1L 17 f4verview Rd 4.07 miles ESE Same as location IL 31A Eckman Rd 4.57 miles SE Same as location il 4K Conowing Dam Power 8.61 miles SE Same as location IL House Roof 23 Peach Bottom 150* 1.01 rniles SSE Same as location IL Sector Hit 27 N. Cooper Road 2.68 miles S Same as location 1L B-5

i

.i

TABLE B-1

Sample Collection and Analysis Program for the Radiological Environmental Monitoring Program for Peach Bottom Atomic Power Station,1995 j

, Location Location Description Distance & . Collecten Method and Frequency Analysis & Frequency l Directen from Performed-Consultant ,

l PBAPS Vents  ;

i 48 Macton Substadion 4.99 miles SSW Same as loceGon 1L i 3A Delta, PA Substellon 3.62 miles SW Same as location IL , '

49 PB-Conestone Line 4.05 miles WSW Same as location 1L 50 TRANSCo Purrying 4.99 mges W Same as locadon 1L

[*

8tadon 41 Fin Substeden 3.98 mNes WNW Same as locadon 1L f

i 26 Sieb Road 4.23 miles NW Same as loceelon 1L i 68 Hollwood Darn Power 5.78 miles NW Same as location IL House Roof 4? Muddy Run Envir. 4.13 miles NNW Same as location IL Lahoretary Distait and Spedal Interest 43 Drumore TowneNp 5.00 miles NNE Same as location IL 1

5 Wakelloid, PA 4.64 miles E Some as locadon IL 3

16 Natungham, PA 12.72 mies E Same as locadon IL Substagion (Control) 24 Harrisvine, MD 10.91 m5es ESE Same as location IL '!

Substellon (Control) i 46 Broad Creek 4.48 mNes SSE Same as lacedon 1L B-6

TABLE B-1: Sample Collection and Analysis Program for the Radiological Environmental Monitoring Program for Peach Bottom Atomic Power Station,1995 Location Location Description Distance & Collection Method and Frequency Analysis & Frequency Directen from Performed--Consultant PBAPS Vents 47 Broad Creek Scout 4.26 miles S Same as locanon IL Camp 18 Faum Grove, PA 9.86 miles W Same as location 1L 19 Red Lion, PA (Control) 20.21 mies WNW Same as location IL OC Laboratory Monhly from Decenter twough March when cows are off pasture.

,g: .

B-7

- _ _ _ _ _ _ _ _ - . - - - - _ _ . _ . - - _ - - - - - - - - _ _ _ - - - - _ _ _ - _ _ _ ~ - - - -

_ . . - - - _ _ - - - v- r - - - - _a m - 1 .. -- _-_ - - - , - - - - - - - - . _ _ _ _ _ _

NN NNE NW NE 1E WNW ENE 4 #1 4

l

'lO -1LL

,j W *

.,s E 1NN 1 A/12 WSW elf ESE 11 IJ 2#

SW SE 1 go\#

@ SSW SSE

/ \

9@

l Figure B-1 l Environmental Sampling Locations Within One

! Mile of the Peach Bottom Atomic Power Station,1995 I B-8

h

, N 61 NW 43 NNE 7 68 -  ;

NW * % e15 NE

• 44 72 e 26 k D WN 22' ENE

• ' 32 e45 51 g

- *a I W '

' 1

,4 E

@' *)

43 c 23 L eN 3-1 wsW 74 e3A I ESE 27

@m 31A s 46 47' 48 5 uite aAoiu ,s

! ssW  %+

s L f

136 4To j

\%'

1 4L 4K I

Figure B-2 Environmental Sampling Locations Between One and Approximately Five Miles from the Peach Bottom Atomic Power Station,1995 B-9

-s n - -- +*6. w -,-wh-=-. a----.2-- *--'u -+'1-'+as a ---r n-- ~,--"'L--- -= ' = > ' = - - *"* =>~- '

R~

\

\

+

tP l b s,, 'Q ,

8 . -

/, > cg

1. .5 ii e

tm

e. is b

.o 5 8'E oo

• LLI W

w E

w m8R m E "

W o '

/ i w

e a

E aC o m h E .c

• m o n ,

m@ .

8 # m D.

> ee

1. E m eE

~

R

• eB o

' ]E wa

,J -

E e

o I .

e -

o z e 5

$ e

\ ,

• 3 *

/

.-. . . . - r ,a.-.- - - -.- . . . . . ~~. ---~-..nn.-- -- - .. . ..- . - ~ . - - - - . . . ..-.. . - . - . . . . _ . . . - .

l 1 1

l l

I l

l f

APPENDIX C DATA TABLES AND FIGURES PRIMARY LABORATORY l

I i

f I

l t

l i

l

APPENDIX C: DATA TABLES AND FIGURES - PRIMARY LABORATORY TABLES Table C-l.1 Concentrations of Tritium in Surface Water Samples Collected in the Vicinity of Peach Bottom Atomic Power Station,1995.

' Table C-l.2 Concentrations of Gamma Emitters in Surface Water Samples Collected in the Vicinity of Peach Bottom Atomic Power Station,1995.

Table C-II.1 Concentrations of Gross Beta Insoluble in Drinking Water Samples Collected in the Vicinity of Peach Bottom Atomic Power Station,1995.

l Table C-II.2 Concentrations of Gross Beta Soluble in Drinking Water Samples Collected in the Vicinity of Peach Bottom Atomic Power Station,1995.

Table C-II.3 Concentrations of Tritium in Drinking Water Samples Collected in the Vicinity of Peach Bottom Atomic Power Station,1995.

Table C-II.4 Concentrations of Gamma Emitters in Drinking Water Samples Collected in the Vicinity of Peach Bottom Atomic Power Station,1995.

Table C-Ill.1 Concentrations of Gamma Emitters in Fish Samples Collected in the Vicinity of Peach Bottom Atomic Power Station,1995.

Table C-IV.1 Concentrations of Gamma Emitters in Sediment Samples Collected in the Vicinity of Peach Bottom Atomic Power Station,1995.

Table C-V.1 ' Concentrations of Gross Beta in Air Particulate Samples Collected in the Vicinity of Peach Bottom Atomic Power Station,1995.

Table C-V.2 Monthly and Yearly Mean Values of Gross Beta Con-

- centrations (E-3 pCi/cu. meter) in Air Particulate Samples Collected in the Vicinity of Peach Bottom Atomic Power Station,1995.

C-i j

Table C-V.3 Concentrations of Gamma Emitters in Air Particulate Samples Collected in the Vicinity of Peach Bottom Atomic Power Station,1995.

{

Table C-VI.1 Concentrations of l-131 in Air lodine Samples Collected in the Vicinity of Peach Bottom Atomic Power Station,1995.

Table C-Vil.1 Concentrations of I-131 in Milk Samples Collected in the Vicinity of Peach Bottom Atomic Power Station,1995.

Table C-Vil.2 Concentrations of Gamma Emitters in Milk Samples Collected

in the Vicinity of Peach Bottom Atomic Power Station,1995.

Table C-Vill.1 Quarterly TLD Results for Peach Bottom Atomic Power j Station,1995.

Table C-Vill.2 _ Mean TLD Results from Peach Bottom Atomic Power Station

[ Site Boundary, Middle, and Outer Rings,1995.

Table C-Vill.3 Summary of the Ambient Dosimetry Program for Peach 1

Bottom Atomic Power Station,1995.

i Table C-IX.1 Summary of Collection Dates for Samples Collected in the

, Vicinity of Peach Bottom Power Station,1995.

t l

FIGURES l Figure C-1 Monthly Insoluble Gross Beta Concentrations in Drinking i .

Water Samples Collected in the Vicinity of PB APS,1995.

4 i

Figure C-2 Monthly Soluble Gross Beta Concentrations in Drinking Water

Samples Collected in the Vicinity of PBAPS,1995.

Figure C-3 Mean Annual Cs-137 Concentrations in Fish Samples Col-lected in the Vicinity of PBAPS,1971-1995.

i

Figure C-4 Mean Semi-Annual Cs-137 Concentrations in Sediment Samples Collected in the Vicinity of PBAPS,1971-1995.

i Figure C-5 Mean Weekly Gross Beta Concentrations in Air Particulate

Samples Collected in the Vicinity of PBAPS,1995.

! l

,5 C - 11 i  !

1 i Figure C-6 Mean Monthly Gross Beta Concentrations in Air Particulate Samples Collected in the Vicinity of PBAPS, 1970-1995.

Figure C-7 Mean Annual Cs-137 Concentrations in Milk Samples Collected in the Vicinity of PBAPS, 1971-1995.

Figure C-8 Mean Quarterly Ambient Gamma Radiation Levels (TLD) in '

s the Vicinity of PBAPS,1973-1995. -

i 4

C - lii

l I

i i

l

! TABLE C-I.1 CONCENTRATIONS OF TRITIUM IN SURFACE WATER SAMPLES COLLECTED l

IN THE VICINITY OF PEACH BOTTOM ATOMIC PONER STATION, 1995 RESULTS IN UNITS OF PCI/ LITER 2 2 SICatA COLLECTION 1LL 13ag PERIOD .

JAN-MAR 95 90 a 70 100 a 70 APR-JUN 9D 70 e 70 80 a 70 JUL-SEP 95 110 2 70 140 a 70 OCT-DEC 95 120 a 70 70 2 70 MEAN 100 e 50 100 2 60 1

l 1

l 1

1

.l l

i C-1

TABLE C-I.2 CONCENTRATIONS OF GAMMA EMITTERS IN SURFACE WATER SAMPLES COLLECTED IN THE VICINITY OF PEACH BOTTON ATOMIC PONER STATION, 1995 RESULTS IN UNITS OF PCI/ LITER z 2 SIGNA COLLECTION K-40 MN-54 CO . t 8 FE-59 CO-60 ZN-65 STC PERIOD ILL JAN 95 20 2 10 0.4 1.0 -0.8 0.9 0 2 2 -0.3 1.0 -4 2 2 FEB 95 20 2 10 -0.1

• 0.7 0.1 2 0.6 0

• 1 0.1 2 0.7 -3 z2 MAR 95 23 2 8 -0.8

• 0.7 -0.5 2 0.7 0 t 1 0.3 2 0.7 0 m2 APR 95 20 2 10 -1 2 1 0.2

• 0.9 1 2 2 0.8 1.0 -4 2 2 MAY 95 30 2 10 -0.5

• 0.9 -0.1 2 0.9 2

• 2 0

• 1 -1 2 2 JUN 95 20 2 20 1 2 2 0 2 2 -2 4 -1 e2 3 e4 JUL 95 20 10 0.5 t 0.9 0.9

• 0.9 1 2 -0.3

• 0.9 -1 2 2 AUG 95 20 2 10 0.1 0.9 -0.6

• 0.8 -1 2 -0.1 0.8 -4 2 SEP 95 21 a9 -0.1 a 0.7 0.1 0.6 0 2 1 0.2 0.7 -2 1 OCT 95 0 2 10 -0.5 2 0.7 -0.4 a 0.6 0 *1 -0.2 0.7 -4 2 2 NOV 95 0 2 10 -0.4 0.7 -0.4 2 0.6 0 *1 -0.3 0.7 -7 2 2 DEC 95 0

• 10 0.5

• 0.8 -1.4

• 0.9 2 2 2 -0.2 0.8 -6 2 2 MEAN 15 2 21 -0.1 1.3 -0.3

• 1.1 0 a2 -0.1

• 0.7 -3 2 5 IMM JAN 95 20 2 20 -1

• 2 -1

• 2 1

• 3 0

• 2 -5

• 4 FEB 95 20 10 -0.1 2 0.9 0.0 2 0.8 1 2 2 0.3 0.8 -5 2 MAR 95 30 10 -0.4 2 0.9 -1.6 0.9 2 2 2 -0.8 0.9 0 2 2 APR 95 20 2 10 0.0 2 0.8 -0.1 0.7 0 2 2 -0.2 2 0.7 -3 2 2 MAY 95 20 2 10 0.5

• 0.8 0.0

• 0.7 1

• 1 -0.5 0.7 -2

• 2 JUN 95 20 30 0 '

• 2 0 2 2 4 4 -1 2 2 -9 4 JUL 95 29 2 8 -0.6 m 0.7 -0.5 0.6 0 2 1 -0.3

• 0.6 -3 1 AUG 95 35

• 9 0.8 0.8 -1.1 a 0.8 2

• 2 0.3 2 0.8 -7 2 2 SEP 95 20 2 10 -1 *1 0.2 2 1.0 0 2 0 2 1 -5 2 OCT 95 0 2 10 0.0 2 0.9 -0.5 2 0.9 0 2 0.4

• 0.9 -3 2 2 NOV 95 10 2 10 0.0 2 0.8 -0.2

• 0.8 -1 *2 0.3 0.9 -6 2 DEC 95 -3 9 0.1

• 0.6 -0.6 2 0.6 1 2 1 0.0- 0.7 -5 2' MEAN 18 2 22 -0.2

• 1.2 -0.5 1.1 1 e2 -0.1

• 0.8 -4 2 5 C-2

TABLE C-I.2 CONCENTRATIONS OF GAMMA EMITTERS IN SURFACE WATER SAMPLES COLLECTED IN THE VICINITY OF PEACH BOTTOM ATONIC PONER STATION, 1995 RESULTS IN UNITS OF PCI/ LITER t 2 SIGNA COLLECTION ZR-95 NB-95 CS-134 CS-137 BA-140 LA-140 STC PERIOD 1LL JAN 95 1 2 0.2 1.0 0.2 2 1.0 1 1 0 2 4 -1 2 FEB 95 0 a1 -0.1 0.7 -3.7 2 0.8 0.1 0.7 -2 2 3 -1 1 MAR 95 0 2 1 1.8 2 0.9 0.0 2 0.8 -0.3 0.7 -4 3 0 2 1 APR 95 -1 2 2 0.8 2 1.0 -1 1 0 1 -3 4 0 2 2 MAY 95 0 a2 0.1 2 0.9 -5 2 1 -0.4

• 0.9 -1 4 0 2 JUN 95 -2 3 1 2 -1 2 1 2 2 5 2 9 -1 2 4 JUL 95 -2 2 1 0.9

• O.9 0.3 0.9 0 a1 -1 4 0 2 2 AUG 95 1 a2 -0.5 2 0.9 -0.4 0.9 -0.1 0.9 -1

• 5 1 2 SEP 95 -1 2 1 -0.1

• 0.7 0.0 2 0.8 -0.4 2 0.8 0

• 3 1 1 OCT 95 0 a1 0.3 2 0.7 -4.3 2 0.9 -0.2 0.7 -2 2 3 -1.0 0.9 NOV 95 0 2 1 0.5 0.7 -6.7

• 0.9 -0.3 2 0.7 -1 2 3 -0.8

• 1.0 DEC 95 0 s2 0.9 2 0.9 1 1 -0.6 0.8 -2

• 4 0 2 1 MEAN O 2 2 0.4 1.2 -1.7 2 5.1 0.0

• 1.1 -1 2 4 -0.1

• 1.2 1MM JAN 95 1 a3 1 2 2 0 2 -1

• 2 -5

• 7 -4 2 4 FEB 95 0 2 2 0.2

• 0.8 -0.7 0.9 0.4 2 1.0 -1 3 0 2 MAR 95 -1 *2 3 2 1 0.2 2 1.0 -1.7

• 0.9 0

• 4 -1 2 APR 95 1 2 1 0.8 0.7 -0.3

• 0.8 -0.6

• 0.8 0 e3 -1 1 MAY 95 0 2 1 0.2

• 0.7 -0.7 2 0.8 -0.3 2 0.9 -3 3 2 1 JUN 95 0- 2 3 -1 2 2 0

• 2 0 2 2 -3 2 8 -5 2 4 JUL 95 0

• 1 0.9 2 0.7 0.1

• 0.7 -0.1 2 0.7 0 2 3 -1 2 1 AUG 95 0 2 1 1

• 1 -0.9 2 0.9 -0.2 0.8 1

• 5 -1 2 2 SEP 95 0 2 2 0

• 1 0 2 1 0 2 1 0 4 -1 2 OCT 95 -1 e2 -2 e1 -6 1 0.0 0.9 1 *3 0 1 NOV 95 0 m1 0.0 0.9 -7 2 1 0.4 2 0.9 2 4 0 2 1 DEC 95 0 e1 0.3 0.7 -5.3

• 0.8 -0.2 2 0.7 -1 2 3 -1 2 1 MEAN O 2 1 0.4 2.4 -1.7 5.4 -0.3 1.2 -1 4 -1 3 C-3

. . -- c..- - . - . _ - ,_. . . . - . _ - . - . . . - - - . . - = - . . . - . - - - . . . - ... -

TABLE C-II.1 CONCENTRATIONS OF GROSS BETA INSOLUBLE IN DRINKING MATER SAMPLES COLLECTED IN THE VICINITY OF PEACH BOTTOM ATOMIC POWER STATION, 1995 RESULTS IN UNITS OF PCI/ LITER a 2 SIGMA COLLECTION 4L 6I PERIOD JAN 95 0.4 a 0.7 0.5

• 0.7 FEB 95 -0.4 a 0.9 -0.7 a 0.9 MAR 95 -0.1 a 0.9 1.2 a 0.9 APR 95 -0.1 a 0.9 0.4 a 1.0 MAY 95 0.2 a 0.8 0.3 a 0.8 JUN 95 1.4 a 0.8 0.6 a 0.8 JUL 95 0.2 a 0.9 0.1 a 0.9 AUG 95 0.0 a 0.9 -0.6 a 0.8 SEP 95 -0.4 a 0.8 0.8 z 0.9 OCT 95 0.2 a 0.8 1.1 a 0.9 NOV 95 1 a1 0.1 a 1.0 DEC 95 -0.9 a 0.9 -0.6 a 0.9 MEAN 0.2 a 1.4 0.3 a 1.3 TABLE C-II.2 CONCENTRATIONS OF GROSS BETA SOLUBLE IN DRINKING MATER SAMPLES COLLECTED IN THE VICINITY OF PEACH BOTTOM ATOMIC POWER STATION, 1995 RESULTS IN UNITS OF PCI/ LITER a 2 SIGNA COLLECTION 4L 6I PERIOD JAN 95 2.2 a 0.9 1.7 a 0.9 FEB 95 1 a1 1 a1

l. MAR 95 1 a1 2 a1 l APR 95 3 a1 3 a1 MAY 95 2 a1 2 a1 i JUN 95 2 a1 1 a1 )

JUL 95 2 a1 4 a1 l AUG 95 3 a1 5 a1 l

SEP 95 4 a1 4 a1 OCT 95 4 a1 3 a1 NOV 95 2 a1 2 a1 DEC 95 1 a1 1 a1 MEAN 2.2 a 2.1 2.4 a 2.3 TABLE C-II.3 CONCENTRATIONS OF TRITIUM IN DRINKING MATER SAMPLES COLLECTED IN THE VICINITY OF PEACE BOTTOM ATOMIC POWER STATION, 1995 RESULTS IN UNITS OF PCI/ LITER a 2 sItatA l

COLLECTION 4L 6I PERIOD JAN-MAR 95 90 a 70 170 a 70 l APR-JUN 95 150 a 70 30 a 70 l JUL-SEP 95 110 a 70 60 a 70 OCT-DEC 95 60 a 70 -10 a 70 MEAN 100 a 80 60 a 150 l l C-4 i

l

TABLE C-II.4 CONCENTRATIONS OF GAMMA ENITTERS IN DRINKING NATER SAMPLES COLLECTED IN THE VICINITY OF PEACM BOTTON ATOMIC POWER STATION, 1995 RESULTS IN UNITS OF PCI/ LITER z 2 SIGNA COLLECTION K-40 MN-54 CO-58 FE-59 CO-60 STC PERIOD ZN-65 4L JAN 95 25 9 0.3 2 0.7 -0.2 2 0.7 0 2 1 -0.2 a 0.7 -5 3 2 FEB 95 40 2 10 -0.1 2 0.9 -0.7

• 0.8 -1 2 -0.3 0.8 -5 2 MAR 95 40 10 -0.6 2 0.9 0.7

• 0.9 1

• 2 0.9 t 0.9 2

• 2 APR 95 30 10 0.1 e 1.0 -0.9 2 0.8 0 2 -0.1 t 0.9 -4 2 2 MAY 95 30 20 0 a2 0 a1 -1 2 3 2 2 -4 2 3 JUN 95 30 2 10 0 e1 -1 2 1 0

• 2 0 *1 -2 2 2 JUL 95 22 8 -0.2 2 0.8 -0.4 a 0.6 1

• 1 -0.2 a 0.7 -3 2 1 AUG 95 20 2 10 -0.4 2 0.9 0.1 a 0.9 -1 2 2 -0.1

• 0.9 -5 2 2 SEP 95 0

• 20 0

• 2 0 *2 3 4 -2 2 2 -1 4 OCT 95 -10

• 10 -0.5 2 0.8 0.2 2 0.8 3 t 2 0.7 a 0.8 -5

• 2 NOV 95 -20 9 -0.7 e 0.6 -0.3 0.6 0 2 1 -0.1 t 0.7 -3 2 DEC 95 0 2 10 -0.2 0.9 0.4

• 0.9 -1 2 2 0.6 2 1.0 -5

• 2 MEAN 17

• 39 -0.2

• 0.7 -0.1

• 1.0 0

• 3 0.1 2 1.7 -3

• 4 6I JAN 95 0 2 30 -2 2 1 2 2 2 4 2 0

• 2 t 4 FEB 95 15 a8 -0.6 0.7 -0.2 0.8 1 1 0.4

• 0.7 1 2 2 MAR 95 5

• 8 0.3 0.7 .-0.7 a 0.7 0

• 1 -0.4

• 0.7 0 2 APR 95 12 2 9 0.5 0.7 0.3 2 0.7 0 2 2 0.0 e 0.8 0 2 2 MAY 95 30

• 10 -0.4 e 1.0 -0.1

• 0.8 -2 e2 -0.6 0.9 -6

• 2 JUN 95 10 2 20 -1 *2 0

• 1 1 2 3 1 a2 -3

• 3 JUL 95 23 2 9 0.1 a 0.6 -0.1 e 0.7 0 2 1 0.3 0.8 -2 2 2 AUG 95 16 2 7 0.2 2 0.6 -0.3 2 0.7 0 m1 0.5 0.6 -3 2 1 SEP 95 30

• 10 -0.4

• 1.0 0.1 2 0.9 -1

• 2 0.3 0.9 -3 2 2 4

OCT 95 0 a 10 0.1 a 0.7 -0.1 2 0.7 1 *1 -1.0 0.7 -4 2 2 NOV 95 -10 m 10 -0.5

• 0.8 -0.2

• 0.7 1 2 2 0.6 0.8 -6 2 DEC 95 10 e 20 -0.2 2 0.9 -0.6 e 1.0 1 2 0.4

• 1.0 -3 2 3' MEAN 12 a 22 -0.3 2 1.4 -0.1 a 0.7 0 *2 0.3 1.6 -2 5 I

C-5

TABLE C-II.4 CONCENTRATIONS OF GAISEA EMITTERS IN DRINKING MATER SAMPLES COLLECTED IN THE VICINITY OF PEACH BOTTOM ATOKIC PONER STATION, 1995 RESULTS IN UNITS OF PCI/ LITER 2 2 SIGMA COLLECTION ZR-95 NB-95 CS-134 CS-137 BA-140 LA-140 STC PERIOD

_____ _______________ _a___________ _____________ _____________ _____________ _____________ _____________

4L JAN 95 0 2 1 0.5

• 0.8 -3.9 0.8 -0.1

• 0.7 0

• 3 1 1 FEB 95 0 t 1 0.1 0.9 0.5 2 1.0 0 2 1 3 2 3 0 1 MAR 95 0

• 2 4 2 1 0 1 -0.3 2 1.0 1

• 4 0 1 APR 95 1 2 2 1.3 2 0.9 -1 2 1 0 2 1 3

• 4 -1 2 2 MAY 95 1 2 2 -1 a1 -1 2 2 0 1 -4 2 5 0 2 2 JUN 95 0

• 2 1

• 1 -1

• 1 1

• 1 1 2 4 1

• 2 JUL 95 0 2 1 0.0

• 0.7 0.2 a 0.7 -0.1 0.8 -1

• 3 0 2 1 AUG 95 1

• 2 -1

• 1 0.5

• 0.9 0.6

• 0.9 4 5 -1 2 SEP 95 0 *3 1

• 2 0 2 2 1 2 0 t 7 2 3 OCT 95 0 m1 0.2

• 0.8 -9 1 -0.4 2 0.9 -3 2 3 -1 1 NOV 95 1 2 1 0.0 2 0.6 -3.5

• 0.8 -0.1 0.6 1

• 2 -0.2

• 0.8 DEC 95 1 2 2 -1

• 1 -6

• 1 -0.4

• 1.0 2 2 4 1 *1 MEAN O e1 0.4 2 2.7 -2.0 t 6.0 0.0 1.0 1 5 0.1 1.8 6I JAN 95 3 2 3 2 2 1

• 2 1 2 2 3 8 -1

• 4 FEB 95 1 2 1 0.3

• 0.8 0.0

• 0.7 0.4

• 0.8 1 .2 3 0 e1 MAR 95 0 1 0.5 2 0.8 0.2 2 0.8 -0.7 0.8 0

• 3 1 2 1 APR 95 0 t 1 -0.1 0.7 -3.1

• 0.8 0.6

• 0.7 2 3 0

• 1 MAY 95 -1 2 1 0.6

• 0.9 -1

• 1 -1 2 1 2 2 4 1 2 2 JUN 95 2 e2 -1 2 1 1

• 1 0

• 1 1

• 5 -1 2 3 JUL 95 0 2 1 0.3 2 0.8 0.0

• 0.8 -0.1

• 0.8 0 3 0 1 AUG 95 0 2 1 0.7 2 0.7 -0.2 0.7 -0.6 0.6 -1 2 4 1 2 1 SEP 95 0

• 2 0.9

• 0.9 0.1 1.0 0 2 1 0' 2 4 1 1 OCT 95 0 *1 , 0.3 0.7 -4.9 2 0.9 -0.7 0.7 3 3 -0.1 0.9 NOV 95 1 *1 0.3 2 0.8 -6.6

• 1.0 0.2 0.8 1 3 0.1 2 0.9 DEC 95 1 *2 0 e1 -7 1 0 1 -2

• 4 0 2 2 MEAN 1 *2 0.5 1.3 -1.7 m 5.9 -0.1

• 1.0 1 3 0.1 2 1.3 C-6

TABLE C-III.1 CONCENTRATI0tts OF GABOR ENITTERS IN FISN SANFLES COLT.ECTED IN TEE VICINITY OF PEACE BOTTORE ATOBEIC F0WER STATIOtt, 1995 RESULTS IN UttITS OF FCI/RG WET e 2 SIGeth COLiaCTIOtt R-40 set-54 CO-58 FE-59 CO-60 EN-65 Cs-134 Cs.137 STC FERIOD

---.. .-----....-- .. .----- ......-- ..... --- _ .....--...... -----........ ---_ ---- =-= ....----...-- ----- _ _ = - _ = - _ - -

4 FREDATOR 06/28-06/28/95 3300 e 300 2 e5 -3 e5 0 e 10 2 a6 0 e 20 0 *6 3 e6 11/08-11/08/95 4000 e 400 -2 *4 0 e4 2 e9 0 e4 -20 e 10 -10 e4 3 e4 30 BAN 3700 e 1000 0 e4 -1 e5 -1 e8 1 e3 -10 e 20 -5 e1 3 eO BOTT00E FREDER 06/22-06/26/95 2500 e 200 1 e5 -3 e5 10 e 10 -1 a6 -10 e 20 4 e5 1 e6 11/08-11/16/95 3100 e 300 0 e4 -4 e5 0 e 10 -1 e5 0

• 10 3 e5 3 e5 DEBAN 2000 e 800 1 e1 4 e1 10 e 10 -1 a0 0 e 10 4 e1 2 e3 6 FREDATOR 06/27-06/27/95 3400 e 300 1 a5 0 e5 0 e 10 7 e6 -30 e 20 2 *6 4 e5 11/06-11/06/95 3600 e 400 3 e5 -3 e5 10 e 10 2 a5 -20 e 10 2 a5 -4 e5 ISAN 3500 e 300 1 a5 -1 e5 0 e 10 4 e7 -30 e 10 2 e0 0 e1 DOTTott FREDER 06/22-06/22/95 2400 e 200 1 a4 0 e4 10 e 10 0 e5 -10 e 10 -15 e5 4 e4 10/16-10/24/95 2900 e 300 -3 e4 0 e4 0 e 10 -1 e5 20 e 10 -21 a5 8 e5 NBAN 2700 e 700 -1 e6 0 e1 0 e 10 0 e1 -10 a0 -18 e8 6 e6 C-7

TABLE C-IV.1- CONCENTRATIONS OF f2kma EMITTERS IN SILT SAMPLES COLLECTED IN THE VICINITY OF PEACH BOTTOM ATOMIC PONER STATION, 1995 RESULTS IN UNITS OF PCI/KG DRY z 2 SIGMk COLLECTION BE-7 K-40 CO-60 CS-134 C8-137 RA-226 TH-232 STC PERIOD 4J 06/29-06/29/95 70 2 70 12000 2 1000 40 2 20 3 2 8 100 2 10 1300 2 300 680 2 70 11/16-11/16/95 -60 2 80 10000 2 2000 20 2 20 10 2 10 360 2 40 2300 a 400 1200 2 100 MEAN O 2 190 15000 2 8000 30 2 30 6 2 9 230 2 370 1000 e 1400 940 2 740 4T 06/29-06/29/95 700 2 200 21000 2 2000 0 2 20 10 2 20 240 2 30 2600 2 500 1500 2 100 11/16-11/16/95 200 2 100 22000 2 2000 30 2 20 0 2 10 220 2 30 2400 t 500 1400 2 100 MEAN 400 2 700 22000 2 1000 10 40 10 2 0 230 2 30 2500 2 30J 1500 2 100 6F 06/29-06/29/95 -10 2 70 11000 2 1000 2 9 5 2 10 100 2 20 2100 2 100 870

• 90 11/16-11/16/95 400 2 100 14000 2 1000 10 2 10 0 2 10 310 2 30 3200 * $00 1600 2 200 MEAN 170 2 510 13000 2 4000 4 2 6 5 *0 200 2 30C 2700 2 1600 1240 m 1030 C-8

. - .- - - - - - _ - ~

d TABLE C.V.1 CONCENTRATIONS OF GROSS BETA IN AIR PARTICULATE SAMPLES COLLECTED IN THE VICINITY OF PEACH BOTTOM ATOMIC POWER STATION, 1995 RESULTS IN UNITS OF E-3 PCI/CU METER 2 2 SIGMA.

GROUP I GROUP II GROUP III WEEK 1B 12 2 3A 22G1 01 17 s4 18  : 4 17 4 15 s4 15 a4 02 26 4 20 s4 29 *5 27 4 13 s4 03 4 a3 4 s3 6 s3 5 2 3 5 s3 04 13 2 4 16 4 16 *4 13 *4 12 s3 05 21 2 4 17 4 22 2 4 19 s4 14 s4 06 22 2 4 16 2 4 19 2 4 19 2 4 21 2 4 07 20 2 4 18 s4 19 e 4 19 4 17 s4 08 24 s4 18 s4 19

• 4 19 2 4 11 s3 09 12 s4 10  : 4 8 s4 10 *4 13 2 4 10 15 2 4 17  : 4 14 *3 16 24 15 s4 11 30 a5 25 s5 24 s4 23 s4 19 s4 12 12 a4 9 3 7 a3 8 s4 11 s4 13 16 s4 18 4 18 *4 18 2 4 17 s4 14 21 2 4 19 a3 19 3 21 a4 18 2 4 15 16 2 4 11 4 16 s4 15 a4 17 4 16 16 s4 17 4 15 s4 13 2 4 13 4 17 14 s3 14 s3 11 s3 12 2 3 11 a3 18 12 2 3 10 2 2 13 s3 11 s3 12 s3 19 13 s3 9 a3 14 2 3 10 2 3 6 s3 20 10 2 3 13 s1 9 2 3 10 2 3 14 2 4 21 13 s4 16 s4 14 2 4 13 a4 12 2 4 22 11 s4 8 s4 12 s4 13 s4 13 2 4 23 12 2 4 12 s4 12 s4 11 s4 10 4 24 14 s3 14 s3 10 a3 12 2 3 16 4 25 21 2 4 21 24 23 2 4 25 a4 13 2 4 26 9 s3 8 3 9 s3 9 2 3 12

• 3 27 16 s5 15 *5 14 2 4 14 a5 17

• 4 28 16 2 4 18 4 20 a5 16 4 24

• 4 29 23 2 5 20 s5 23 s5 23 a5 14

• 4 30 21 2 4 21 2 4 22 2 4 18 a4 24 s4 31 21 2 4 24 s4 20 2 4 25 a4 16 4 32 12 a4 10 s4 11 a3 11 s4 11 s4 33 19 4 21 s4 20 a4 18 2 4 20 4 34 17 4 20 18 {

2 4 2 4 19 s4 12 s3 '

35 19 s4 19 2 4 21 a4 20 a4 19 s3 36 (1) 25 a4 26 4 26 4 20 a5 37 22 2 4 21 2 4 19 s4 19 s4 13 *3 38 15 2 4 11 2 4 12 s4 11 s3 12 s4 l 39 17 *4 15 a4 22 s4 is a4 16 s4 40 19 s5 20 s5 16 5 18 5 16 2 5 41 19 s4 19 s4 19 4 18 4 21 s4 42 16 s5 19 5 16 s5 14 2 5 9 4 43 17 2 4 16 2 4 16 2 4 16 4 19 4 44 18 5 16 s4 16 2 4 15 2 4 17 2 4 45 15 a4 16 2 4 20 4 17 4 20 2 4 46 13 4 11 2 3 15 s3 12 3 17 s4 47 22 2 4 21 a4 20 2 4 21 2 4 17

• 4 48 19 a2 20 s2 21 2 2 19 s2 17 s2 49 23 a4 22 s4 24 s4 24 4 le  : 4 50 20 a5 20 a5 21 s5 25 a5 20 4 51 19 4 18 a4 19 *4 19 2 4 13 s3 52 18 4 14 a3 16 2 4 14 3 14 4 MEAN 17 *9 16 9 17 s 10 16 10 15 a8 (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-9

-5r

?

TABLE C-V.3 CONCENTRATIONS OF GAbsth ENITTERS IN AIR PARTICULATE SAMPLES COLLBCTED IN TER VICINITY OF PEACE BOTTott ATONIC POWER STATION, 1995 RESULTS IN UNITS OF E-3 PCI/CU METER e 2 SIGNA COLLECTION 35-7 K-40 CS-134 CS-137 RA-226 TB-232 STC PERIOD

... . . - _== .. .....__ -- - .........--.. - ___- - - - = = . . . . _ _ . - - . . . . - _ - = _ - - = ....

la 12/30-03/30/95 80 e 20 0

• 20 0 e1 0 e1 -20 s 20 -2 e5 03/30-07/02/95 100 e 20 11 e8 -0.6 e 0.8 0.4 e 0.9 20 e 20 2 e3 07/02-09/29/95 60 e 20 0 e 20 0 e2 -1 e2 10 a 20 -1 e5 09/29-12/30/95 60 e 10 0 e 10 -2.3 e 1.0 0.2 a 0.7 0 e 10 0 a3 MEAN 70 e 40 2 e 13 -0.7 e 2.3 0.0 e 1.0 0 e 30 0 e3 1E 12/30-03/30/95 60 e 10 10 e 10 0.6 e 0.7 0.6 e 0.7 10 e 20 3 e3 03/30-07/02/95 70 e 20 10 e 10 0.9 e 0.9 0.6 e 0.5 20 e 10 1 e3 07/02-09/29/95 60 e 20 10 e 20 0 e1 -1 e1 20 e 20 -2 e5 09/29-12/30/95 60 e 20 10 e 10 -0.8 e 0.9 -0.3 a 0.9 -10 e 20 2 e3 NBAN 60 e 10 10 e 10 0.2 e 1.5 0.0 e 1.3 10 e 30 1 a4 2 12/30-03/30/95 80 e 20 20 e 20 0.6 e 0.9 -1 e1 20 e 20 0 e6 03/30-07/02/95 110 e 30 0 e 20 -1.1 e 1.0 -0.5 e1 0 a 20 1 e5 07/02-09/29/95 80 a 20 10 e 10 0.3 e 0.9 -0.1 a 0.6 30 e 10 0 e3 09/.19-12/30/95 70 e 20 0 e 10 0 e1 -1 e1 0 e 10 0 *3 MEAN 80 e 40 10 e 20 -0.1 e 1.5 -0.4 e 0.5 10 e 30 0 e1 k 3A 12/30-03/30/95 03/30-07/02/95 70 60 e

e 20 20 10

-10 e

e 10 20 0.7 0

e 0.8 e1

-0.4

-0.6 e 0.6 e 0.9 30 0

e e

20 20

-1 2

e3

• 5#

07/02-09/29/95 70 e 20 10 e 20 1 e1 -1 e1 0 e 20 0 e4 09/29-12/30/95 40 e 20 0 e 20 -3 e2 -1 e1 0 e 20 -1 a4 HEAN 60 e 30 0 e 20 -0.3 a 3.7 -0.8 e 0.8 10 e 30 0 *2 2201 01/03-04/03/95 90 e 30 10 e 10 0 e1 1 e1 10 e 20 -3 e6 04/03-07/03/95 70 e 20 10 e 20 0 e1 -0.5 e 1.0 30 a 20 -2 e4 07/03-10/02/95 80 e 10 20 e 10 -0.4 e 0.7 0.1 a 0.6 30 e 20 2 e2 10/02-01/02/96 50 e 20 20 e 20 -1 e1 0.1 e 1.0 10 e 20 2 e4 MEAN 70 e 30 10 e 10 -0.4 e 0.5 0.1 a 0.9 20 e 20 0 e5 C - 11

TABLE C-VI.1 CONCENTRATIONS OF I-131 IN AIR IODINE EkMPLES COLLECTED IN THE VICINITY OF PEACH BOTTOM ATOMIC POWER STATION, 1995 RESULTS IN UNITS OF E-3 PCI/CU METER z 2 SIGMA GROUP I GROUP II GROUP III WEEK 13 12 2 3A 2201 01 10 e 20 -10 10 0 2 20 0 s 10 0

• 20 02 10 z 20 0 2 20 0 2 20 -10 s 20 10 2 20 03 10 e 10 -11 10 0 10 -10 10 -10 z 20 04 10

• 20 0

• 20 -10 2 20 0 10 -10 10 05 -10 2 20 5 10 0 2 20 0 2 10 10 2 10 06 -10 2 10 20 10 0 m 20 20 2 20 10 2 10 07 10 2 10 1  : 10 0 20 0 10 10 2 20 08 0 2 10 1 m9 0 10 0 2 10 5 2 6 09 -10 10 0 2 10 0 2 20 0 2 10 -2 8 10 10 10 0

• 20 10 10 10 2 10 1 z9 11 -20 2 10 0 2 10 10 s 20 0 2 20 10 s 10 12 0 2 20 -10 2 10 0

• 20 0 z 10 -10 a 20 13 0 s 20 0 s 10 0 2 20 0 2 10 0 s 20 14 0 2 10 7 z 10 0

• 20 0 10 -10 2 20 15 10 a 20 -10 a 10 0 10 10 -

10 0 10 16 0 9 5 m 10 -10 2 20 10 2 10 0 2 10 17 0

• 10 0 2 20 -6

• 9 0 2 20 -1 z 10 19 -10 2 20 0 s 10 0 e 20 -10 10 0 10 19 10 10 -10 s 10 0 s 20 -10 s 20 2 z 10 20 0 2 10 -10

• 10 -5 a 10 0 e 20 5 *9 21 0 m 10 0

• 20 -10 a 20 0 a 10 0 z- 10 22 0 s 10 0 2 10 0 2 10 10 z 20 4 9 23 -10 2 20 10 10 0 10 0 z 10 1 8 24 10 z 10 0 z 10 -2 z9 0 2 10 10 z 10 25 -10 a 20 10 a 10 10 a 20 -10 z 10 20 a 10 26 1 2 7 2 2 7 -3 7 0 e 10 0 z 10 27 10 a 20 0 2 10 -10 z 20 -10 2 20 7 *9 29 1 a 10 20 z 20 10 2 20 0 2 20 0 z 10 29 -10 2 20 -10

• 10 0 2 10 20

• 20 -10 z 10 30 0 2 10 0 z 10 0 s 20 -4 9 3 *7 31 -10 2 20 1 9 -10 s 10 2

• 9 -1 7 32 -10

• 20 20 a 10 0 a 20 10 10 4 2 9 33 10 2 20 0 a 20 10 z 20 0 s 20 -10 z 10 34 0

• 20 -8 z9 -10 a 10 0 a 10 -3 z8 35 -ic 10 4 9 0 20 0 a 10 -10 z 10 36 (1) 10 2 10 0 10 -20 s 20 10 z 20 37 20 2 30 0  : 10 10 e 20 0 2 20 0 10 38 -10

• 20 0 10 10 s 20 0 e 20 0 s 10 39 0 2 20 -1  : 8 0  : 10 0 z 10 12 2 10 40 -10 2 20 0 10 0 2 20 10 s 20 -3 10 41 0 z 10 0 e 10 0 10 -10 2 10 0 10 42 0 a 20 0 z 10 0 2 20 -10 2 20 -5 *9 43 0 a 20 -10 a 20 10 a 20 2 9 -5 10 44 0 m.10 -4 s 10 -10 s 20 1 2 9 -6  : 9 45 10  : 10 -2 8 0 2 10 1  : 7 10 2 10 46 0 10 10 a 10 0 2 20 10 a 20 -7 a 10 47 -10 z 20 -10 2 10 0 2 10 10 2 20 2 2 8 48 -1 8 1 a6 0 a 10 2 2 9 -2 2 7 49 -20 10 10 e 20 10 a 20 0

• 20 -10 e 10 50 -20 2 20 0 2 20 -10 a 10 0 s 30 -1  : B 51 10

• 20 0 10 -10 e 10 0 a 20 2

• 7 52 0 m 20 0 z 20 0 2 10 -10 e 20 0

• 10 MEAN 0 2 17 1 2 13 0 a 11 0 14 0 2 12 (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-12

m ._. x m . _ _

m 8

4 M M M M u e e e e

! O O O O e e e e i O *e O re 8M i e e a e 0 0 0 O O O l I 0 0 8 8 M M M es et 3 $ e e a e e e e O O O O O 8 8 0 8 40 e 40 40 de B 4 0 0 4 8 0 0 O es es O O 4Q 3 e e e o e 0 O O O O O t 8 8

8 N N N N 90 g e e e e a t O O O O O 4 e e e e es 6

e f

8 O ed og M O 3 3 e e o e e 4 O O O O O 6 0 Kt l nit t 8 09 he e e N. N N e Ne e N eNeNeNe Ne Ne n H n t9 He 4% a e N e eree n N

e e eO OOOOOOOOOOO S0000000 O I e 0 9 46 40 40 e 42 40 el el de el 48 46 48 4e e el de el 4146 90 0 0 C$

Q g s(

.4 3 e 90 00,4. 404 94 - 94 . O e . e e o e e e e e e e e e e e e e e 8O 90000000000 00000000 O 8 0 0 6 0 $ g e 0

I 0 M M M e4 n

$ e e e e e e O O O O O 4

0 48 48 to e de 4

0 0

0 O H O H H

' As 4 e e e a e 4 O O O O O 4

e a i 4494949M MMetM MMegM M sg et #9 gg 4 e e e e e o e e e e o e e e e e e 9OOOOOOOOOOOO OOOO O 4 es 8 de 48 e is e e 40 de te es de te 8

de e e e #4e es w

S

.m e ne,4e9eede noOenee eveerseO. O.

e e4e ne e.e M. e. D il 0000000000000 0000 0 8 4 4 4 8 4 0 4 6 0 0 I M 69 M es

$s e e H. e e 8 O O O O O N9

g. e e e e e en m

Q A 94 e4 e4 e4 H . e4 e a P4 O e e o A U O O O O O U $ $

5 H

Rl .

. .e e< . .9 .e H M t e e .

6 O O O O O 8

4 48 e el 40 41 8

IFA 8

4 ll 9 e4 O e4 O O 3 e e e e e 4 O O O O O E I e U

H i M.f4e M. M. Me M M M. Mo M. M o M. M. Me et. M. 89. M. M. M #9 11n.

e s e.t H 90D0000000000 OOOOOOOO O i

4840404040404141 4040414f41 40 414140 48 e 4e el 48 de i 0

0 M

1H E

d t

0 0 O e4 O pt e4 #9 M N ed M O e4 O e0 e e a e o e e o e e e e e e 40000000000000 0 0 0 0 0 00000000 MNOMOMOM o e e e a e 4

O O

e 94 U M 4 md U e e4 O 4 Se As e i

i Me M a f4M e eM e Mo Me M. M Me M e Me eM MMMM.MMMM e e e e e et e 3 M b e

e i 9000000000000 OOOOOOOO O O i

H i e 40 to es es 414e es de 4s es to to es es 4e er es 4s to te es 4*Ob O 8 4

9 0>> N e

0 0

H e l'3 Oe Oe Oe M eO eM o Oe M e e e4eOev4e O M. S. O e4e r0 e4 94 e M e r0 O. 3 E g i OOOOOOOOOO4sOO GOOOOOOO O O HH 0 e e 4 e e 6 0 0 M NO E B to H 8 4 m ll> l 0 en eN N.N Ne H90N t% N N N N e% N M N N O g e e e eNeNe N e Ne N iP4 g

ge t e e e e e o e o e O 30000000000000 00000000 O M 0 0 N Pe 0 0 to to el es el 4141 et 40 40 40 el el 41 40 40 e e # et el e S0 4 52 i.gO i

. . .de4 . - - - e4 0 94 4 4 O O O a .0 0 a .t O g e e e e e e a e e e o a e e e e e e e e a e M 4OOOOOOOOOOOOO OOOOOOOO O

• 8 e f 6 0 8 0 m

44 M 3

> 0 0

M 4 W O

e e en in e m en en en in am en en en an m m en en en en en en en a W 4 m m A m m A R 4h # A A & S & M 44 S & R & S 44 N4%%%%%%%%%%%%%%%%%%%%%%

d 80 eg Q MM M e4 Ft O c4 9MOOM Mm e wemW f e4 M W e P4 W & M e e4 re O e'e see 4 M e4 et M H M O M O et ye e4 3%%%%%%%%%%%%%%%%%%%%%% w at I e=0 M M W W in en 4D 49 b f* f* O O O th & O O H v4 M N 0 O O O O O O O O O O O O O O O O O M e4 e4 og M

TABLE C-VII.2 CONCENTRATIONS OF GAIAEA EIEITTERS IN MILK SAMPLES COLLECTED IN THE VICINITY OF PEACE TsOTTOK ATONIC POWER STATION, 1995 RESULTS IN UNITS CF PCI/ LITER

• 2 SIGNA COLLECTION K-40 C8-134 C8-137 RA-140 LA-140 STC PERIOD A 02/13-02/13/95 1400 t 100 1

• 2 1 2 2 5 a7 2 2 05/22-05/22/95 1300 2 100 -5 a1 2 1 3 t 4 0 a1 08/13-08/13/95 1400 m 100 -5 a1 0 1 3 2 4 1 a1 10/23-10/23/95 1400 100 -3.8 2 0.9 0.0

• 0.0 0 m3 0.6

• 0.8 MEAN 1400 2 100 -3.3 2 5.8 0.5 a 1.8 3

• 5 1.0 2 1.9 G 02/13-02/13/95 1300

• 100 -1 e1 -1 2 2 1 *5 -2 22 05/22-05/22/95 1400 e 100 -4 1 0 *1 1 a3 -1 1 08/13-08/13/95 1500 a 100 -5 1 0 *1 -2 2 4 0 e1 10/23-10/23/95 1400 m 100 -8 e2 0 a2 -4 2 6 -1 2 2 MEAN 1400 e 200 -5 6 -1 e1 -1 e5 -1 2 2 J 02/13-02/13/95 1400 e 100 -3 e2 1 *2 -1 6 J 2

'![ 05/22-05/22/95 1400 a 100 -3.2

• 0.9 0.2

• 0.8 0 3 0 e1 08/13-08/13/95 1300 a 100 -4 *2 2 2 2 -1

• 6 0* 2 3 10/23-10/23/95 1400 2 100 -3 a1 1 e1 3 a5 1 2 1 MEAN 1400 a 100 -3.4 0.5 1.0

• 1.3 0 4 1 e2 N 02/13-02/13/95 1300 2 100 1 e1 -1 1 0 5 1 *1 05/22-05/22/95 1500

• 100 -7 e1 0 e1 -2 a4 0 2 1 08/14-08/14/95 1400

• 100 -4.1

• 0.9 1.4 2 0.8 0 2 3 -0.4

• 0.9 (1)

MEAN 1400 2 200 -3.5 e 7.9 0.3 2.0 -1 *2 0.1 a 1.4 O 02/13-02/13/95 1400

• 100 1 e2 2 *2 1 *6 2 2 2 05/22-05/22/95 1400 e 100 -8 2 1 0.6 2 0.9 -3 2 3 1 2 1 08/13-08/13/95 1400

• 100 -5 2 2 0 *2 -2 *7 1 2 ,

10/23-10/23/95 1300

• 100 1 *~2 0

• 2 -1 a6 0 2 f MEAN 1400 a 100 -3 2 9 0.5 e 1.7 -1 a4 1 1 (1) SEE PROGRAM EXCEPTION SECTION FOR EXPLAMATION C-14 i

._ . - . . _ . ~. - - - - . - - - . _ - . . . - . _ - - - - _ _ . _ . _ - _ _ - _

1 1

TABLE C-VIII.1 QUARTERLY TLD RESULTS FOR PEACH EDTTOM ATOMIC POWER STATION, 1995 I RESULTS IN UNITS OF MILLI-ROENTGEN /STD. MO. a 2 s.D.

STATION MEAN a JAN-MAR APR-JUN JUL-5EP OCT-DEC CODE 2 8.D. (1) 1A 5.0 a 0.4 5.3 a 0.4 5.1 a 0.2 4.0 a 0.4 4.9 a 0.4 13 4.5 a 0.1 4.5

• 0.3 4.5 a 0.4 4.4 a 0.3 4.5 a 0.7 1C 5.6 a 0.1 5.6 a 0.6 5.6 a 0.7 5.5 a 0.7 5.6 a 0.7 1E 5.0 a 0.3 5.0 a 0.5 5.1 a 0.3 5.1 a 0.4 4.8

• 0.1 IF 6.4 a 0.3 6.4 2 1.0 6.5

• 0.4 6.6 a 0.5 6.2 a 0.2 1G 3.8 a 0.1 3.9

• 0.5 3.8 a 0.1 3.9 a 0.1 3.0 a 0.2 1N b.5 a 0.4 5.6

• 0.9 5.5 a 0.6 5.6

• 0.5 5.2 a 0.2 II 4.3 a 0.3 4.5 a 0.5 4.2 a 0.2 4.3 a 0.5 4.2 a 0.3 1J 6.3 a 0.5 6.1 a 0.5 6.2 a 0.9 6.7

• 0.4 6.3 a 0.2 1L 4.0 a 0.4 4.3 a 0.3 4.1 0.2 3.9 a 0.6 3.8 a 0.2 2 5.0 a 0.5 5.1 a 0.5 4.7

• 0.3 5.3 a 0.4 5.1 a 0.9 3A 3.6 a 0.3 3.7

• 0.3 3.4 z 0.3 3.7 a 0.3 3.7 a 0.2 4K 3.3 a 0.2 3.5 a 0.2 3.3 a 0.2 3.3 a 0.0 3.3 a 0.2 5 5.1 a 0.4 5.1 a 0.7 5.3 a 0.1 5.2 a 0.1 4.8 a 0.4 6B 4.2 a 0.3 4.3

• 0.3 4.1 a 0.2 4.1 a 0.2 4.4 a 0.2 1NN 6.1 a 0.5 6.4 z 0.5 6.3 a 0.3 6.1 a 0.5 5.8 a 0.5 14 5.3 a 0.1 5.3 a 0.8 5.3 a 0.5 5.4 a 0.2 5.3 a 0.4 15 5.3 a 0.3 5.0 a 0.2 5.3 a 0.4 5.3 a 0.2 5.4 a 0.9 16 5.6

• 0.7 5.6 a 0.7 5.2 a 0.7 6.0 a 0.7 5.5 a 0.3 17 6.3 a 0.7 6.8 a 0.4 6.0 a 0.6 6.3 a 0.5 6.2 a 0.3 18 5.0 a 0.4 5.9 a 0.4 5.6

• 0.4 5.7 a 0.5 6.0 a 0.7 19 5.5

• 0.6 5.8 a 0.5 5.2 a 0.4 5.6 a 0.5 (2) 22 5.7 a 0.4 6.0 a 0.5 5.5 a 0.4 5.6 a 0.4 5.7 a 0.9 23 5.6 a 0.2 5.6 a 0.5 5.5 a 0.3 5.7 a 0.3 5.7

• 0.2 24 4.2 a 0.3 4.2 a 0.2 4.0 a 0.2 4.3 a 0.6 4.3 0.2 26 6.2

• 1.0 6.7 a 0.1 5.6 a 0.3 6.5 a 0.7 6.0

• 0.7 27 5.8 a 0.5 6.1 a 0.1 5.S a 0.? 5.6 a 0.2 5.6 a 0.4 32 5.9 m 0.4 6.0 a 0.3 5.8 a 1.2 6.1 a 0.5 5.7

• 0.3 31A 4.3 a 0.3 4.3 a 0.3 4.3 a 0.1 A.5 a 0.3 4.2 a 0.1 40 6.5

• 1.2 7.0 a 0.8 6.0 a 0.5 1.0 a 0.4 6.0 a 0.2 42 4.4 a 0.1 4.5

• 0.3 4.4

• 0.4 4.4 a 0.2 4.5 a 0.7 43 6.3 a 0.4 6.4 a 0.4 6.0 a 0.4 6.4 a 0.7 6.2 a 0.3 44 5.1 a 0.4 5.1 a 0.4 4.9

• 0.2 3.4 a 0.3 5.0 a 0.5 45 5.8 a 0.6 5.7

• 0.5 6.0 a 0.4 6.1 a 0.4 5.5 a 0.4 46 5.3 a 0.6 5.3 a 0.4 4.9 a 0.4 5.6 a 0.3 5.2 a 0.3 47 6.1 a 0.8 6.0 a 0.1 5.0 a 0.7 6.7

• 0.9 6.0 a 0.8 48 5.5 a 0.3 5.7 a 0.5 5.4 a 0.3 5.6 a 0.4 5.4 a 0.6 49 5.6 a 0.3 5.0 a 0.3 5.7 a 0.5 5.6 a 0.6 5.4 a 0.7 50 6.6 a 0.6 6.4 a 0.4 6. 8 a O '. 4 7.0 a 0.4 6.4 a 0.4 51 5.8 a 0.4 5.7

• 0.3 5.6 a 0.3 6.1

• 0.2 5.8 a 0.7

1. MEAN AND 'MO TIMES THE STANDARD DEVIATION OF THE QUARTERLY RESULTS.

2. SEE PROGRAM EXCEPTIONS SECTION FOR EXPLkMATION.

C - 15

s .. _ . . _ _ _ . . . ~_ .- ._ . _ . .. _ _ . ~ . .

TABLE C.VIII.2 1995 MEAN TLD RESULTS FROM PEACH BOTTOM ATOMIC PONER STATION r FOR THE SITE BOUNDARY, MIDDLE, AND OUTER RINGS l RESULTS IN UNITS OF MILLI-ROENTGEN /STD. MO.

• 2 STANDARD DEVIATIONS OF THE STATION DATA SAMPLE EXPOSURE SITE MIDDLE RING OUTER RING t TYPE PERIOD QUARTERLY JAN-MAR 1995 5.4 2 1.9 5.4 1.8 5.4 e 1.6 APR-JUN 1995 5.2

• 1.8 5.2

• 1.7 5.0 1.4 JUL-SEP 1995 5.3 2 2.1 5.5 2 1.9 5.4

• 1.5 OCT-DEC 1995 5.1

• 1.7 5.3

• 1.6 5.3 e 1.7 t

TABLE C-VIII.3

SUMMARY

OF THE 1995 AMBIENT DOSIMETRY PROGRAM FOR PEACH BOTTON ATOMIC PONER STATION RESULTS IN UNITS OF MILLI-ROENTGEN /STD. MO.

PERIOD PRE-OP

• SAMPLE NO. OF SAMPLES PERIOD PERIOD MEAN MEAN TYPE LOCATION ANALTEED MINIMUM MAYTMUM z 2 S.D. 2 2 S.D. (1)

QUARTERLY SITE 52 3.8 7.0 5.2 a 1.8 5.4 1.7 [

MIDDLE RING 92 3.3 7.0 5.4 2 1.7 5.3 2 1.3 OUTER RING 15 4.0 6.0 5.3

• 1.4 5.7 2 1.8 l

i (1) THE PRE-OPERATIONAL MEAN WAS CALCULATED FROM TLD READINGS 1/07/73 TO 8/05/73.

SITE BOUNDARY RING STATIONS - 1A, 18, 1C, 1D, 1E, 1F, 1G, 1H, l' II, 1J, IL, INN, 2, AND 40.

MIDDLE RING STATIONS - 3A, 4K, 5, 6B, 14, 15, 17, 22, 23, 26, 27, 31A, 32, 42, 43, 44, 45, 46, 47, 48, 49, 50, AND 51.

l OUTER RING STATIONS - 16, 18, 19, AND 24.

C - 16

TABLE C-IX.1 SUtesARY OF COLLECTION DATES FOR SAMPLES COLLECTED IN THE .

VICINITY OF PEACE BOTTOM ATottIC PONER STATION, 1995 SURFACE AND DRINKING MATER (TRITIUM)

COLLECTION 1LL 13GE 4L 6I PERIOD JAN-NAR 95 12/28-03/29 12/28- h/29 12/30-03/30 12/30-03/31 APR-JUN 95 03/29-06/28 03/29-06/28 03/30-0"/02 03/31-07/03 JUL-SEP 95 06/28-09/27 06/28-09/27 07/02-09/29 07/03-09/30 OCT-DEC 95 09/27-01/03 09/37-01/03 09/29-01/06 09/30-01/06 1

\

l l

SURFACE AND DRINKING MATER (GhMdA AND GROSS BETA) I COLLECTION 1LL 1MM 4L 6I PERIOD JAN 95 12/28-02/01/95 12/28-02/01/95 12/30-02/03 12/30-02/03 4 FEB 95 02/01-03/01/95 02/01-03/01/95 02/03-03/03 02/03-03/03 MAR 95 )

03/01-03/29/95 03/01-03/29/95 03/01-03/30 03/01-03/31 '

APR 95 03/29-05/03/95 03/29-05/03/95 03/30-05/05 03/31-05/05 NAY 95 05/03-05/31/95 05/03-05/31/95 05/05-06/02 05/05-06/02 JUN 95 05/31-06/28/95 05/31-06/28/95 06/02-07/02 06/02-07/03 CUL 95 06/28-08/02/95 06/28-08/02/95 07/02-08/04 07/03-08/04 AUG 95 08/02-08/30/95 08/02-08/30/95 08/04-09/01 08/04-09/01 SEP 95 08/30-09/27/95 08/30-09/27/95 09/01-09/29 09/01-09/30 OCT 95 09/27-11/01/95 09/27-11/01/95 09/29-11/02 09/30-11/02 NOV 95 11/01-13/29/95 11/01-11/29/95 11/02-11/03 11/02-10/03  ;

DEC 95 11/29 01/03/?6 11/29-01/03/96 12/03 01/06 12/03-01/06  ;

i e

C - 17 tr

-.- ~~- - .~_ - -. .. ----- - -- - . - - . .. - - - - _- .

i TABLE C-IX.1 SUIEfARY OF COLLECTION DATES FOR SAMPLES COLLECTED IN TEE VICINITY OF PEACE BOTTOM ATOMIC POWER STATION, 1995- l AIR PARTICULATE AND AIR IODIEE +

WEEK 13 '

1E 2 3A 22G1 01 12/30-01/07 12/30-01/07 12/30-01/07 12/30-01/07 01/03-01/09  :

02 01/07-01/14 01/07-01/14 01/07-01/14 01/07-01/14 01/09-01/16 03 01/14-01/21 01/14-01/21 01/14-01/21 04 01/14-01/21 01/16-01/23 01/21-01/27 01/21-01/27 01/21-01/27 01/21-01/27 01/23-01/30 05 01/25-02/03 01/25-02/03 01/25-02/03 01/25-02/03 01/30-02/06 06 02/03-02/10 02/03-02/10 02/03-02/10 02/03-02/10 02/06-02/13 07 02/10-02/17 02/10-02/17 02/10-02/17 02/10-02/17 02/13-02/20  !

08. 02/17-02/25 02/17-02/25 02/17-02/25 02/17-02/25 02/20-02/28 '

09 02/25-03/03 02/25-03/03 02/25-03/03 02/25-03/03 02/20-03/06 10 03/03-03/10 03/03-03/10 03/03-03/10 03/03-03/10 03/06-03/13 11 03/10-03/17 03/10-03/17 03/10-03/17 03/10-03/17 03/13-03/20 12 03/17-03/24 03/17-03/24 03/17-03/24 13 03/17-03/24 03/20-03/27 03/24-03/30 03/24-03/30 03/24-03/30 03/24-03/30 03/27-04/03 14 03/30-04/07 03/30-04/07 03/30-04/07 03/30-04/07 1

04/03-04/10 '

15 04/07-04/14 04/07-04/14 04/07-04/14 04/07-04/14 04/10-04/17

'16 04/14-04/21 04/14-06/21 04/14-04/21 04/14-04/21 04/17-04/24 17 04/21-04/28 04/21-04/28 04/21-04/28 04/21-04/20 04/24-05/01 18 04/28-05/05 04/20-05/05 04/28-05/05 04/28-05/05 19 05/01-05/08 05/05-05/12 05/05-05/12 05/05-05/12 05/05-05/12 05/08-05/15 20 05/12-05/19 05/12-05/19 03/12-05/19 05/12-05/19 21 05/15-05/22 5 05/19-05/26 05/19-05/26 05/19-05/26 05/19-05/26 05/22-05/29  ;

22 05/26-06/02 05/26-06/02 05/26-06/02 05/26-06/02 23 05/29-06/05 -

06/02-06/09 06/02-06/09 06/02-06/09 06/02-06/09 06/05-06/12 24 06/09-06/16 06/09-06/16 06/09-06/16 06/09-06/16 25 06/12-06/19  ;

06/16-06/23 06/16-06/23 06/16-06/23 06/16-06/23 06/19-06/26 l 26 06/23-07/02 06/23-07/02 06/23-07/02 06/23-07/02 06/26-07/03 '

27 07/02-07/08 07/02-07/08 07/02-07/08 07/02-07/08 07/03-07/10 28 07/08-07/14 07/00-07/14 07/08-07/14 07/08-07/14 07/10-07/17 29 07/14-07/20 07/14-07/20 07/14-07/20 07/14-07/20 07/17-07/24 i 30 07/20-07/28 07/20-07/28 07/20-07/28 07/20-07/28 31 07/24-07/31 07/28-08/04 07/20-08/04 07/28-08/04 07/28-08/04 07/31-08/07 32 08/04-08/11 08/04-08/11 08/04-08/11 08/04-00/11 08/07-08/14  ;

33 08/11-08/18 08/11-08/18 08/11-00/10 08/11-00/18 08/14-00/21 34 08/18-08/25 08/10-00/25 08/10-08/25 08/18-00/25 08/21-08/20 1

l 35 08/25-09/01 08/25-09/01 08/25-09/01 08/25-09/01 08/20-09/05 '

36 09/01-09/08 09/01-09/08 09/01-09/00 09/05-09/11 37 09/00-09/15 09/08-09/15 09/08-09/15 09/00-09/15 09/11-09/18 30 09/15-09/22 09/15-09/22 09/15-09/22 09/15-09/22 09/18-09/25 39 09/22-09/29 09/22-09/29 09/22-09/29 09/22-09/29 09/25-10/02 40 09/29-10/06 09/29-10/06 09/29-10/06 09/29-10/06 10/02-10/09 41 10/06-10/13 10/06-10/13 10/06-10/13 10/06-10/13 10/09-10/16 42 10/13-10/20 10/13-10/20 10/13-10/20 10/13-10/20 10/16-10/23 43 10/20-10/27 10/20-10/27 10/20-10/27 10/20-10/27 10/23-10/30 44 10/27-11/02 10/27-11/02 10/27-11/02 10/27-11/02 10/30-11/06 45 11/02-11/09 11/02-11/09 11/02-11/09 11/02-11/09 11/06-11/13 46 11/09-11/17 11/09-11/17 11/09-11/17 11/09-11/17 11/13-11/20 47 11/17-11/24 11/17-11/24 11/17-11/24 11/17-11/24 11/20-11/27 de 11/24-12/03 11/24-12/03 11/24-12/03 11/24-12/03 11/27-12/04 49 12/03-12/10 12/03-12/10 12/03-12/10 12/03-12/10 12/04-12/11 50 12/10-12/16 12/10-12/16 12/10-12/16 12/10-12/16 12/11-12/18

! 51 12/16-12/23 12/16-12/23 12/16-12/23 12/16-12/23 12/10-12/26 52 12/23-12/30 12/23-12/30 12/23-12/30 12/23-12/30 12/26-01/02 C-18 I

m. . . . _ _ . _ . . _ , . - _ . __ _ _ . _ . _ . _ -__ _ . . _ _ - _ _ _ _ _ _

4 TABLE C-IX.1

SUMMARY

OF COLLBCTION DATES FOR SAMPLES COLLECTED IN TEE  !

VICINITY OF PEACE BOTTON ATONIC POWER STATION, 1995 TLD - DUARTERLY 5

JAN-MAR APR-JUN JUL-SEP OCT-DEC l STATION 1995 1995 1995 1995 l t CODE 1A 01/04-03/30 03/30-07/02 07/02-09/29 09/29-01/06 j 15 01/04-03/30 03/30-07/02 07/02-09/29 09/29-01/06 '

ic 01/04-03/30 03/30-07/02 07/02-09/29 09/29-01/06 1E 01/04-03/30 03/30-07/02 07/02-09/29 09/29-01/06 1F 01/04-03/30 03/30-07/02 07/02-09/29 09/29-01/06 10 01/04-03/30 03/30-07/02 07/02-09/29 09/29-01/06 15 01/04-03/30 03/30-07/02 07/02-09/29 09/29-01/06 1I 01/04-03/30 03/30-07/02 07/02-09/29 09/29-01/06 1J 01/04-03/30 03/30-07/02 07/02-09/29 09/29-01/06 1L 01/04-03/30 03/30-07/02 07/02-09/29 09/29-01/06 2 01/04-03/30 03/30-07/02 07/02-09/29 09/29-01/06 3A 01/03-03/30 03/30-07/02 07/02-09/29 09/29-01/06 4K 01/03-03/30 03/30-07/02 07/02-09/29 09/29-01/06 5

63-01/03-03/31 03/31-07/03 07/03-09/30 09/30-01/05 1NN 01/03-03/31 03/31-07/03 07/03-09/30 09/30-01/06 14 01/04-03/30 03/30-07/02 07/02-09/29 09/29-01/06 01/03-03/31 03/31-07/03 0*,T;~09/30 09/30-01/05 15 01/03-03/31 03/31-07/03 07/03-09/30 09/30-01/05.

16 01/03-03/31 03/31-07/03. 07/03-09/30 09/30-01/05 17 01/03-03/31 03/31-07/03 07/03-09/30 09/30-01/05 18 01/04-03/31 03/31-07/02 07/02-09/30 '09/30-01/05 19 01/03-03/31 03/31-07/02 07/02-09/30 22 01/03-03/31 03/31-07/03 07/03-09/30 09/30-01/05 23 01/04-03/30 03/30-07/02 07/02-09/29 09/29-01/06-24 01/03-03/31 03/31-07/03 07/03-09/30 09/30-01/05 26 01/03-03/30 03/30-07/02 07/02-09/29 09/29-01/05 27 01/04-03/30 03/30-07/02 07/03-09/29 09/29-01/05 32 01/03-03/31 03/31-07/03 07/03-09/30 09/30-01/05 31A 01/03-03/31 03/31-07/03 07/03-09/30 09/30-01/05 40 01/04-03/30 03/30-07/02 07/02-09/29 09/29-01/06 42 01/03-03/31 03/31-07/03 07/03-09/30 09/30-01/05 43 01/03-03/31 03/31-07/03 07/03-09/30 09/30-01/05 44 01/03-03/31 03/31-07/03 07/03-09/30 09/30-01/05 45 01/03-03/31 03/31-07/03 07/03-09/30 09/30-01/05 46 01/03-03/30 03/30-07/02 07/02-09/29 09/29-01/05 47 01/03-03/30 03/30-07/02 07/02-09/29 09/29-01/05 48 01/03-03/30 03/30-07/03 07/02-09/29 09/29-01/05 49 01/03-03/30 03/30-07/02 07/02-09/29 09/29-01/05 50 01/03-03/30 03/30-07/02 07/02-09/29 09/29-01/05 51 01/03-03/30 03/30-07/02 07/02-09/29 09/29-01/05 C - 19

FIGURE C-1 MONTHLY INSOLUBLE GROSS BETA CONCENTRATIONS lN DRINKING WATER SAMPLES COLLECTED IN THE VICINITY OF PBAPS,1995 6 . . . . .

l

• INDICATOR-4L -

• CONTROL-61 .

4 . . . -.- -- .'-- .-----' ----.- --- .- -- -- -

.* e  :  :  :  : .  :

,e . . . . . .

.2 - - - - - -: ---- :- -  :- - - - - '- - '

g - ' '

a.

,5

~

+

/ A .

]

g I I I

-2 I I I I I I '

JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC MONTHS

FIGURE C-2 MONTHLY SOLUBLE GROSS BETA CONCENTRATIONS IN DRINKING WATER SAMPLES COLLECTED IN THE VICINITY OF PBAPS,1995 14 . . . . . . . . . .

12 _

INDICATOR-4L .............................................

• CONTROL-61 10 .

8 - - -

.---- ~.-

~

m . . . . .

En  :  :  :  :  :  :  :  :

,g . . . . . . . . . .

R--

6 ---

g

o.  :  : .  :  : . . . .

4 W- -

2y-------,-

r -,----- g m 9-----

n n . . . . . .

(

0  :  : .

. . . . . . i i 1 i i i I I I I i

-2 JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC MONTHS

FIGURE C-3 MEAN ANNUAL CS-137 CONCENTRATIONS IN FISH SAMPLES COLLECTED IN THE VICINITY OF PBAPS, 1971 - 1995 1000 - -

:  : -c  :  :  :  :  :

t -

-o- CONTROL 800 - - - -! - - - - - !- - - - ~- - - -! - - - - - :- - - - - - - .'- - :-

• lNDICATOR m . . . . . . . .

s>8 . . . . . . . . .

e p 600 E,,

m 4oo l . . . .:....

tn _

O -

y _ .

s QQQ

. .. ........ .. .... .....~...... ....... . .. .... .. ... .

O -  :  :  :

3.4 gg -

0 . . .

1

'I ' I I ' I ' ' ' I ' I ' I ' I ' I ' I

-200 ' '

i 71 73 75 77 79 81 83 85 87 89 91 93 95 YEAR

i FIGURE C-4 -

SEMI-ANNUAL CS-137 CONCENTRATIONS IN SEDIMENT SAMPLES COLLECTED IN THE VICINITY OF PBAPS, 1971 - 1995 2500 - -

• 4D (IND.)  :

i 2000 -

+ 4J (IND.) ~~T~~~~:'~~~~1~~~~~?~~~~I~~~~T~~~i~

~'.~~~~'

M

+ 4T (IND.)

9 -  !  !

f- 1500 7 -----------------: --

+ 6F (CON.)

E  :  :  :  :  :

t- , _- . . . . . . . .

u 300g _ . . . . .

En _ . . . .

O _

p

.i __

s, _

5" 500 ----- -- -

- 1 -~' - - - ---------

k e

f 0,

.3 .

3 an

-500  !  !  !  !  !  !  !  !  !  !  !

71 73 75 77 79 81 83 85 87 89 91 93 95 YEAR Station 4D discontinued beginning 1991, No sample collected from Station 4J in 1990

FIGURE C-5 MEAN WEEKLY GROSS BETA CONCENTRATIONS IN AIR PARTICULATE SAMPLES COLLECTED IN THE VICINITY OF PBAPS,1995 50 . . . . . . . . . .

• Group i 40 ---

• Group 11 - ^--

m. -

-!- -i-- .'-~ .......

~~~. ~~i-- :- - - -: -

.cm _

m-

+ Group ill - -

E

,o 30 -- - - - .- -

.a _A: .

x  :  :  :  :  :  : .  :

3 _: 1:  :  :  :  :  :  :

c3 . . ,

% 2 -

20 -

--}--------- ' .

~

- - & {- -: -- -- .

l

c. n . . . . . .~ ..

n, ,- ,

i.u -

10 - -

-}---,- -, --}-

,----f ,--

.-h --- .- -, -,

1:

.I iiI iiI .if ii! .,! ,il ..I i i f i i ii,f ii! .i! .iI ii! iiI ,I O i i i i i i i i i i i i i i i i i 1 4 7 10 13 16 19 22 25 28 31 34 37 40 43 46 49 52 WEEK NO.

l i

FIGURE C-6  !

MEAN MONTHLY GROSS BETA CONCENTRATIONS IN AIR PARTICULATE SAMPLES COLLECTED IN THE VICINITY OF PBAPS, 1970 - 1995 .

10000  : : : ::: .;;;;;  ::::;;;;;,::::7 . ::: ,: : : : :,. . . : :,. : : : :, : : : :, : : :

. . . ....................................... . 1

. ALL STATIONS .

. . .......s . . . .s . . . .s . . . . ............ . ........ ............. ... .

1000 L. . . . ........ . . . . . . . . . .. . . . . .. . . . . .. . . . . ... . . . . . . . : : :.: : : :

e b......t

:.:.:::::::::::::::c.::::::::::.::::.:.:  ::::: ::  :::::::: .

stud . . t ....t ....t . . . .t ....t . . . . . . . . . . . . . . - .. . ..... .. *....

g .

t . ...t

. . . .:....t.

. ...t . . . . . . . .

E .

t . . .

g J2 1 1 - - -

CHERNOBYL 100

3 g

o  :::: :

. . :.:}:.::

g .....

g

....h................

g ......

. , . . . . . , . . . ,. . . . k ...

n

:  : .I..

.N a PBAPS . . . . . .

W 10 7 CRITICALITY } ; ; ; 3.; : , : 3 :3 3 3 ; E '; i : ; 3. 3 : ; 3., . : 3:: g ; i: ,3.::3; .

UNIT 2 09/16/73 ,: :::'...:.:::::::.:.:::::. .::::::. .::::.:

UNIT 3 08/07/74

~;;; ;; , - ;;;; ; ; ;,; ; ; ;;;;

I I I I i 70 72 7'4 76 73 EO 8'2 8'4 8S 83 9'O 92 9'4 96 YEAR

FIGURE C-7 MEAN ANNUAL CS-137 CONCENTRATIONS IN MILK SAMPLES COLLECTED IN THE VICINITY OF PBAPS, 1971 - 1995 20 . . . . . . . . . . .

O DISTANT FARMS

-  :  :  :  :  :  : OINTERMEDIATE FARMS 15

- - - - : - - - - - '. - - - - - :.- - - - - -:. - - - -MNEARBY

.  : - - - - .FARMS -----

n- . . . . . . . .

cp .

g .

5 10 -

-:- - - : : - - - -:- - - - - -:- - - - - ? - - - - + - - - - --------

- ---? -

o Q- _

s . . . . . . . . .

5 -----------

- ---. - -~~~--

,  ! , I , I ,  ! , I ,  ! ,  ! , f . I I , I ,

O i i i i i i i i i i i i 71 73 75 77 79 81 83 85 87 89 91 93 95 YEAR

I i FIGURE C-8 MEAN QUARTERLY AMBIENT GAMMA RADIATION (TLD)

LEVELS IN THE VICINITY OF PBAPS, 1973 - 1995 l 10 . . . . . . . . . . . . . . .

l . . . . . . . . . . . . . . .

l t

. .

• SITE PBAPS - -

.c 9

~~'.~'. ~'-

• MIDDLE RING CRITICALITY - - - - - -

, g . . . . . . .

l o j unir 2 os/is/7s j j  :

j .

, -o- OUTER RING E .

unir 3 os/o7/74 . . .

. 8 - ;- --------- - - - - .- -

'O en  :  :  :  :  :  :  :  :  :  : __:  : . .  :  :

s en  :

j C

. c

. (:  : .

i. . . .

. m -

1 C 7 _....<...l.. . -

1 9-.*..:.-Q. . ... '

y

_ }(-f e .

3 , } . . . . .

C -

c L

l $. - - '

%a' ^.

g g - .

~~

~

O 6 ' i-

- :- - 3 - :- - -

- :- . %n( ~

g . . . .

jkt't 54 '

6 .

lg  ;

(

Es c.:  :.. ..:...:..:..: .:. .:...:...:..:..:.... . . ..:.  :. '

.-..: .. i  !

g . . .

4 f l t I

l l t I

d i t i

l l l i

t i l i

t i l l

9 i l 1

f l i i

f i t i

t i l i

1 1 8 I

O l i i

I l l i

I l 3 i

f l l i

f i t i

if I i

l 9 1 i

I l l i

t i l I

l l t i

f I l t

G l i 73 75 77 79 81 83 85 87 89 91 93 95 YEAR

i i

4 4

(

I

.t I

I s

4

)

i i

4 J,

4 4

,r j

i, 1

J 4

i i

1 2

4 2

i 4

APPENDIX D A

E 4

a DATA TABLES AND-FIGURES COMPARISON LABORATORY .

5 e i i

f .

4 e

4 s

4 i

I 1

l APPENDIX D: DATA TABLES AND FIGURES - COMPARISON LABORATORY l l

TABLES s Table D-l.1 Concentrations of Gross Beta insoluble in Drinking Water Samples

] Collected in the Vicinity of Peach Bottom Atomic Power Station,  !

i 1995.

l j Table D-l.2 Concentration of Gross Beta Soluble in Drinking Water Samples.

1

- Collected in the Vicinity of Peach Bottom Atomic Power Station, i 1995.

l l Table D-l.3 Concentrations of Gamma Emitters in Drinking Water Samples  !

Collected in the Vicinity of Peach Bottom Atomic Power Station, )

1995. '

Table D-II.1 Concentrations of Gross Beta in Air Particulate Samples Collected in the Vicinity of Peach Bottom Atomic Power Station,1995.

Table D-II.2 Concentrations of Gamma Emitters in Air Particulate Samples  !

Collected in the Vicinity of Peach Bottom Atomic Power Station, i 1995. I l

Table D-Ill.1 Concentrations of I-131 by Chemical Separation and Gamma Emitters in Milk Samples Collected in the Vicinity of Peach Bottom Atomic Power Station,1995.

Table D-IV.1 Summary of Collection Dates for Samples Collected in the Vicinity of Peach Bottom Atomic Power Station,1995.

FIGURES Figure D-1 Comparison of Monthly Insoluble Gross Beta Concentrations in Drinking Water Samples Split Between GPU and TBE,1995.

Figure D-2 Comparison of Monthly Soluble Gross Beta Concentrations in Drinking Water Samples Split Between GPU and TBE,1995.

Figure D-3 Comparison of Weekly Gross Beta Concentrations in Air Particu-late Samples Collected from Co-located PBAPS Locations 1 A and 1Z,1995.

D-i

The following section contains data and figures illustrating the analyses performed by the quality control laboratory. Duplicate samples were obtained from several locations and media and split between the primary laboratory, GPU Nuclear and the quality control laboratory, Teledyne Brown Engineering (TBE). Comparison of the results for most media were within expected ranges, though occasional differences were seen:

TBE's results of gross beta insoluble and soluble in drinking water samples were slightly higher than the results from GPU (Figures D-1 and D-2, Appendix D). The differences were probably due to variations in the respective laboratory's ar;alytical ,

procedures. TBE counts the samples for 50 minutes, GPU counts for 100 minutes. l 1

The gross beta results for air particulate samples collected at the co-located stations 1Z and 1 A compared very well (Figure D-3, Appendix D). No significant diferences were noted. Both laboratories use Cs-137 as a calibration source. 1 f

l

)

i i

i I

\

j D-1 1

TABLE D-I.1 CONCENTRATIONS OF GROSS BETA INSOLUBLE IN DRINKING WATER SAMPLES i COLLECTED IN THE VICINITY OF PEACE BOTTON ATOMIC POWER STATION, 1995 l RESULTS IN UNITS OF PCI/ LITER 2 2 SIGBEA  ;

L COLLECTION 4L PERIOD JAN 95 0.4 2 1.0 FEB 95 0.1 a 0.5 NAR 95 0.0 2 0.9 APR 95 0.1 2 0.9 NAT 95 0.5 2 0.5 JUN 95 0.9 2 0.5 JUL 95 0.2 2 0.5 AUG 95 -0.1 2 0.5 SEP 95 0.3 a 0.5 OCT 95 0.4 2 0.5 NOV 95 0.7 2 0.5 DEC 95 -0.2 2 1.0 NEAN O.3 a 0.7 TABLE D-I.2 CONCENTRATIONS OF GROSS BETA SOLUBLE IN DRINKING WATER SANPLES COLLE::TED IN THE VICINITY OF PEACE BOTTON ATOMIC POWER STATION, 1995 j RESULTS IN UNITS OF PCI/ LITER e 2 SIGUL COLLECTION 4L PERIOD JAN 95 2 2 1 FEB 95 2.8 a 0.9  ;

NAR 95 2 2 1 i APR 95 1 2 1 NAT 95 2.6 e 0.9 [

JUN 95 2.3 2 0.8 JUL 95 3.2 2 0.9 AUG 95 2.9 2 0.9 SEP 95 5 2 1 OCT 95 5 2 1 NOV 95 2.7

• 0.9

. DEC 95 1 2 1 NEAN 2.7 2 2.5 D-2

TABLE D-I.3 CONCENTRATIONS OF GADOUL INITTERS IN DRINKING WATER SAMPLES COLLECTED IN THE VICINITY OF PEACH BOTTON ATONIC POWER STATION, 1995 RESULTS IN UNITS OF PCI/ LITER 2 2 SIGUL COLLECTION K-40 356- 5 4 CO-58 FE-59 CO-60 IN-65 STC PERIOD 4L FEB 95 10 a 10 0.6 2 0.0 0.4 2 0.9 1 2 2 0.1 2 0.0 0 2 2 NAY 95 -10 2 10 -0.1 2 0.5 -0.3 2 0.6 0 2 1 0.4 2 0.5 1 2 1 JUN 95 -10 2 20 -0.2 2 0.8 0.1 2 0.9 -1 2 2 -0.1 2 0.8 0 2 2 JUL 95 -40 2 10 0.3 2 0.8 -0.1 2 0.9 -1 2 2 -0.1 2 0.7 0 2 2 AUG 95 -10 2 10 0.9 2 0.9 0 2 1 0 2 2 -0.3 2 0.9 4 2 2 SEP 95 -10 a 10 0.1 2 0.8 0 2 1 1 2 3 0.9 2 0.8 1 2 2 OCT 95 -40 2 10 0.6 2 0.8 -1 2 1 -1 2 3 -0.5 2 0.7 1 2 2 NOV 95 0 2 10 0.4 2 0.8 -0.1 a 0.8 0 2 2 0.4 2 0.8 0 m2 DEC 95 -1 2 6 0.0 2 0.5 0.0 2 0.6 0 2 1 0.7 z 0.6 1 2 1 4L MEAN -13 2 33 0.3 2 0.8 -0.1 2 0.6 0 2 1 0.2 2 0.9 1 2 3 COLLECTION ER-95 NB-95 CS-134 CS-137 BA-140 LA-140 STC PERIOD 4L FEB 95 1 2 2 1 2 1 0.4 2 0.8 0.7 2 0.8 1 2 6 -1 2 3 NAY 95 2 2 1 0.5 2 0.6 -0.1 2 0.6 -0.2 2 0.6 3 2 3 0 m1 JUN 95 1 2 2 0.5 2 0.9 0.4 2 0.9 0.2 2 0.8 3 2 6 0 2 2 JUL 95 0 2 2 0.7 2 0.9 -0.3 2 0.8 0.7 2 0.8 -1 2 7 1 2 3 AUG 95 0 2 2 1 2 1 -1 2 1 1 2 1 -3 2 6 1 2 2 SEP 95 3 2 2 0 2 1 0.3 2 0.8 -0.9 2 0.9 0 2 20 -5 2 8 OCT 95 1 a2 0 2 1 0.1 2 0.8 0.7 2 0.8 20 m 20 10 2 10 NOV 95 1 2 2 0.1 2 0.8 0.4 2 0.8 -0.6 2 0.9 -1 a3 0 2 1 DEC 95 -1 2 1 0.1 2 0.6 0.3 2 0.6 0.0 2 0.6 -2 2 3 0 2 1 4L MEAN 1 2 2 0.5 2 0.7 0.1 2 0.8 0.2 2 1.3 2 2 14 -1 2 5 D-3

TABLE D-II.1 CONCENTRATIcets OF OROSS BETA IN AIR PARTICULATE SANPLES COLLECTED IN TEE VICINITY OF PEACE BOTTON ATOMIC POWER STATION, 1995 RESULTS IN IfMITS OF F 3 PCI/CU NETER a 2 SIGNA l

i NEEK 1A '

01 19 a3 02 20 a4 03 1 2 3 04 16 a4 05 21 2 3 06 21 a3 07 18 a3 08 23 a3 09 15 a3 10 16 a3 11 27 a4 12 10 a3 13 16 2 4 14 19 a3 15 15 a3 16 17 a3 17 15 a3 le 14 a3 19 11 2 3 20 10 {

a3 J 21 14 a3 22 14 a3 23 14 a3 l 24 16 a3 25 22 s3 26 9 a2 27 18 a4 28 19 a4 29 27 a4  !

30 24 a3 31 26 2 4 32 15 a3 33 29 a4 34 17 a3 35 22 a3 36 26 a3 37 21 a3 38 18 a3 39 20 a3 40 21 a3 41 20 m3 42 23 a3 43 16 a3 44 18 a4 45 19 a3 46 17 a3 47 21 2 3 du 23 a3 49 24 a4 50 20 m4 51 22 a3 52 15 a3 MEAN 19 a 11 D-4

TABLE D-II.2 CONCENTRATIOtts OF GhletA EltITTERS IN AIR PARTICULATE SAMPLES COLLECTED IN THE VICINITY OF PEACH BOTTON ATONIC POWER STATICit, 1995 RESULTS IN UNITS OF E-3 PCI/CU METER 2 2 SIGRA COLLECTIOtt BE-7 K-40 CS-134 CS-137 RA-226 STC PERIOD TE-228 1A 12/30-03/30/95 73 2 7 10 m5 0.2 a 0.3 -0.2 2 0.3 1 a5 0.4 2 0.5 03/30-07/02/95 09 m9 0 2 3 0.0 2 0.2 0.0 2 0.2 1 2 3 -0.5 s 0.3 07/02-09/29/95 74 2 7 65 2 8 0.2 2 0.4 0.0 2 0.4 -4 a5 0.6 2 0.4 09/29-12/30/95 51 2 6 -2 2 7 -0.3 2 0.4 0.0 2 0.3 2 2 5 -0.1 2 0.4 MEAN 72 2 31 18 m 63 0.0 2 0.5 -0.1 2 0.2 0 2 5 0.1 a 1.0 G

D-5

TABLE D-III.1 CONCENTRATIONS OF I-131 BY CHEMICAL SEPARATION AND QAMMA EMITTERS IN MILK SAMPLES COLLECTED IN THE VICINITY OF PEACE BOTTON ATOKIC POWER STATION, 1995 RESULTS IN UNITS OF PCI/ LITER 2 2 SIGNA COLLECTION I-131 K-40 CS-134 CS-137 BA-140 LA-140 STC PERIOD A 02/13-02/13/95 -0.05 2 0.04 1300 2 100 2 2 2 2 2 3 1 2 9 0 s4 05/22-05/22/95 -0.05 2 0.04 1600 2 200 0 2 3 1 2 3 3 2 8 1 2 3 08/13-08/13/95 -0.01 2 0.07 1500 2 100 1 2 2 0 2 2 0 2 6 -1 2 2 10/23-10/23/95 0.03 2 0.05 1400 m 100 -1 2 2 1 2 2 2 2 5 -1 m2 MEAN -0.02 2 0.07 1500 2 300 1 22 1 2 2 1 2 3 0 mi G 10/23-10/23/95 -0.06 2 0.06 1500 2 100 1 2 3 2 2 3 -5 2 8 2 2 3 J 02/13-02/13/95 -0.04 a 0.05 1500 2 100 0 2 2 2 2 2 -1 2 6 -1 2 2 05/22-05/22/95 -0.01 2 0.04 1500 2 200 1 2 2 -1 2 2 2 27 1 2 3 08/13-08/13/95 -0.06 2 0.05 1500 2 100 1 2 3 2 2 3 1 27 0 2 3 10/23-10/23/95 0.03 2 0.06 1400 2 100 -1 2 3 2 2 3 0 2 8 -2 2 3 MEAN -0.02 2 0.07 1500 2 100 0 2 2 1 2 3 0 2 3 -1 2 2 N 02/13-02/13/95 0.01 2 0.05 1300 2 100 -1 2 3 2 2 3 6 2 8 0 2 3 05/22-05/22/95 -0.15 m 0.05 1500 a 100 -1 2 2 3 2 2 1 2 7 1 2 3 08/14-08/14/95 -0.04 2 0.08 1300 2 100 0 2 2 1 2 2 0 z8 1 2 3 MEAN -0.06 2 0.16 1400 2 200 -1 2 1 2 2 2 2 2 6 1 2 1 D-6

TABLE D-IV.1

SUMMARY

OF COLLECTION DATES FOR SAMPLES COLLECTED IN THE VICINITY OF PEACE BOTTOM ATOMIC POWER STATION, 1995 COLLECTION 4L PERIOD JAN 95 12/30-02/03 FEB 95 02/03-03/03 mar 95 03/03-03/30 APR 95 03/30-05/05 MAY 95 05/05-06/02 JUN 95 06/02-07/02 JUL 95 07/02-08/04 AUG 95 08/04-09/01 SEP 95 09/01-09/39 OCT 95 09/29 11/02 NOV 95 11/02-12/03 DEC 95 12/03-01/06 WEEK 1A WEEK 1A 01 12/30 01/07 27 07/02-07/08 02 01/07 01/14 28 07/08-07/14 03 01/14-01/21 29 07/14-07/20 04 01/21-01/27 30 07/20-07/28 05 01/27 02/03 31 07/20-08/04 06 02/03-02/10 32 08/04-0s/11 07 02/10-02/17 33 08/11-0s/1e 08 02/17-02/25 34 08/18-08/25 09 02/25-03/03 35 08/25-09/01 10 03/03-03/10 36 09/01-09/06 11 03/10-03/17 37 09/0s-09/15 12 03/17-03/24 30 09/15-09/22 13 03/24-03/30 39 09/22 09/29 14 03/30-04/07 40 09/29-10/06 15 04/07 04/14 41 10/06-10/13 16 04/14 04/21 42 10/13-10/20 17 04/21-04/28 43 10/20-10/27 10 04/20-05/05 44 10/27-11/02 19 05/05-05/12 45 11/02-11/09 20 05/12-05/19 46 11/09-11/17 21 05/19-05/26 47 11/17-11/24 22 05/26-06/02 de 11/24-12/03 23 06/02-06/09 49 12/03-12/10 24 06/09-06/16 50 12/10-12/16 25 06/16-06/23 51 12/16-12/23 26 06/23-07/02 52 12/23-12/30 D-7

FIGURE D-1 COMPARISON OF MONTHLY INSOLUBLE GE OSS BETA CONCENTRATIONS IN -

DRINKING WATER SAMPLES (4L) SPLIT ElETWEEN GPU AND TBE,1995 4

~

+ GPU 3 -

• TBE h 2 i 2 o ,

o j'\

E1 ,g

~

'a - s A

I s ,- s g -& s

'A _ m - d' s_ - s h

i 1 l i I l I l i l f 1 2 3 4 5 6 7 8 9 10 11 12 MONTH

FIGURE D-2 COMPARISON OF MONTHLY SOLUBLE GROSS BETA CONCENTRATIONS IN '

DRINKING WATER SAMPLES (4L) SPLIT BETWEEN GPU AND TBE,1995 6

-o- G PU 5 ,A 4

• TBE ,

s 4 f "s

• f \

f \

3 ~ ,

+

E A A, '

A

, s s

f 'sg, O 2b A m o m g e ,

N /

1 al ,

0 1 2 3 4 5 6 7 8 9 10 11 12 MONTH

FIGURE D-3 WEEKLY GROSS BETA CONCENTRATIONS IN AIR PARTICULATE SAMPLES COLLECTED FROM CO-LOCATED PBAPS LOCATIONS 1 A AND 1Z,1995 50 . . . . . . . . .

• 1 A (TBE) . .

s.

40

- - - 1Z (GPU)

'---:--!---i

. . . i h ,

g _

E - - - - - - -

(3 30 -- - - :- - - - :- - - -: - -

1:--;--. .

-> ( . .

(

.gl3 s .

3 . .

q i .

o q .

~~

20 - - :- --

g g

) .

is

. e uu -

l 10

- [ly . . . . . . . . . . . . . .

3,. . . . . . . . . . . . . . .

. sl .l ..l ,! ,,I ,.I i.I ,,f ,.I iiI . . I I l I I I 0

, i i , i i i i . , . , i 1 i i i i i i i i i i i i i i i e i 1 4 7 10 13 16 19 22 25 28 31 34 37 40 43 46 49 52 WEEK NO.

APPENDIX E SYNOPSIS OF ANALYTICAL PROCEDURES l

s

l l

l APPENDIX E: SYNOPSIS OF ANALYTICAL PROCEDURES The following section contains a description of the analyticallaboratory procedures along with an explanation of the analytical calculation methods used by,GPU Nuclear and Teledyne Brown Engineering to obtain the sample activities.

l l

1 l

l

)

l l

E-1

a DETERMINATION OF GROSS BETA ACTIVITY IN WATER SAMPLES (TOTAL SUSPENDED AND DISSOLVED FRACTIONS)

GPUN Environmental Radioactivity Laboratorv ,

l This describes the process used to measure the radioactivity of water i samples without identifying the radioactive species present. No chemical  !

separation techniques are involved.

For surface and drinking water samples,400 ml of the sample is filtered under vacuum through a 0.45 micron filter.' This filter represents the insoluble portion of the sample. The filter is dried and mounted on a planchet. The filtrate which represents the soluble portion of the sample is evaporated on a hot plate, and the residue is transferred and dried on another planchet.

The planchets are counted for 100 minutes in a low-background gas flow proportional counter. Calculation of activity includes a self-absorption correction for counter efficiancy based on the weight of residue on each planchet.

Calculation of Samole Activity and 2 Slama Uncertaintv:

g, C-B 2.22x%xTFx Vx T 2s= 2xA 2.22xQxTFx VxT g 4.66x/B

2.22xEox TFxVxT Where

l 4

R = Activity of sample in picocuries per unit volume or weight.

Volume or weight units are those used for V. l 2s = 2 Sigma Counting Uncertainty LLD = Lower Limit of Detection C = Sample Counts B = Blank Counts E, = Efficiency of the counter i TF = Transmission Factor T = Acquisition time in minutes V = Volume or weight of aliquot analyzed.

4 E-2 i-r

DETERMINATION OF GROSS BETA ACTIVITY 'N WATER SAMPLES (TOTAL SUSPENDED AND DISSOLVED FRACTIONS)  ;

J l

l Teledyne Brown Enoineerino  :

i This describes the process used to measure the radioactivity of water samples without identifying the radioactive species present. No chemical j separation techniques are involved. )

For surface and drinking water samples', one liter of the sample is filtered -

l under vacuum through a 0.45 micron Millipore filter. This filter represents the l l insoluble portion of the sample. The filter is dried and mounted on a planchet.

l The filter which represents the soluble portion of the sample is evaporated on a hot plate, and the residue is transferred and dried on another planchet.

The planchets are counted for 50 minutes in a low-background gas flow proportional counter. Calculation of activity includes a self-absorption l

correction for counter efficiency based on the weight of residue on each planchet.

l Calculation of Samole Activity and 2 Siama Error:

i

$_p 2 5+1 ts Result , t, 3 f j WH (2.22)($(E) (2.22)($(E)

Net Activity Counting Error where:

N = total counts from sample (counts) t, = counting time for sample (min)

B = background rate of counter (cpm)

t. = counting time for background (min) 2.22 = dpm/pCl v = volume in liters E - efficiency of the counter 2 - multiple of counting error

! The MDL is defined as that value equal to the two sigma counting error of the

! result.

i E-3 l

l &~

i

DETERMINATION OF TRITIUM IN WATER BY LIQUID SCINTILLATION COUNTING l GPUN Environmental Radioactivity Laboratorv i

i Seven (7) milliliters of sample is filtered tnrough a 0.45 micron filter into a vial  !

l and mixed with 15 ml of liquid scintillation material and counted for a minimum i

of 480 minutes to determine its activity. The tritium activity is determined by  ;

l measuring the count rate in the beta activity energy spectrum in Region A.

l 20.0 to 2000 represents Region C. If the sample Region C cpm is within 25% of the average background Region C cpm and the sample Quench Indicating Parameter (OIP) is within 20 of the H-3 source OlP the sample has no contamination and the tritium activity may be calculated directly. If not the l sample must be purified before recounting.

Calculation of Samole Activity and 2 Siama Uncertainty: l l g, C-B 2.22x4x VxDF i

! l l l l 2x S + E-1  % T. Ts

! 2s=

l 1

2.22xE x VxDF 3.20x 0 + E-y  % T, Ts

2.22xE,x VxDF i

Where:

l l T. = Total count time of sample in minutes T. - Total count time of background in minutes R = Tritium activity in picoCuries per unit volume (Volume.

units are those used in V) 2s = 2 sigma Uncertainty in the same units as above

( LLD = Lower limit of detection in same units as above j C = Average count rate of sample

6 = Average count rate of background E-4

l l

l E, = Tritium detection efficiency of counter, calculated as i shown below l V = Volume of aliquot l DF = Decay factor, calculated as shown below l

l l -m or DF=e '2

• DT = time difference in years from collection stop date to counting date of sample l The efficiency is c..lculated as follows:

l S-B Asx VsxDFs Where:

l S = Average count rate for the " efficiency determination" standard B = Average count rate of background As = Activity of standard in dpm per unit volume Vs = Volume of standard used l DFs = Decay factor of standard, calculated as follows:

-MnDTs

A*

DFs=e DTs = time difference (in years) between calibration date and counting date t

i i

E-5 9

l DETERMINATION OF GROSS BETA ACTIVITY IN AIR PARTICULATE SAMPLES GPUN Environmental Radioactivity Laboratory After allowing at least a three-day (extending from the sample stop date to the sample count time) period for the short-lived radionuclides to decay out, each air particulate filter paper is placed in a 2-inch diameter stainless steel l planchet and counted using a gas flow proportional counter.

1 Calculation of Sample Activity and 2 Siama Uncertainty:

l g, C-B 2.22xEo xTFxVxT l

2s= 2x@

l 2.22xE ox TFx Vx T tg,p. 4.66x/B 2.22xE ox TFx Vx T l

Where R = Activity of sample in picoCuries per unit volume or weight.

Volume or weight units are those used for V.

2s = 2 Sigma Counting Uncertainty LLD = Lower Limit of Detection C = Sample Counts B = Blank Counts Eo = Efficiency of the counter TF = Transmission Factor of filter (i.e.1.00 for gross beta,0.80

! for gross alpha) l T = Acquisition time in minutes l V = Volume analyzed.

1 E-6

~ - -- - - .- - - - . --- - .

DETERMINATION OF GROSS BETA ACTIVITY IN AIR PARTICULATE SAMPLES Teledyne Brown Enaineerina This describes the process used to measure the overall beta activity of air l particulate filters without identifying the radioactive species present. No chemical separation techniques are involved. Each air particulate filter is placed directly on a 2-inch stainless steel planchet. The planchets are then counted for beta activity in a low-background gas flow proportional counter. 1 Calculation of activity includes an empirical self-absorption correction curve which allows for the change in effective counting efficiency caused by the residue mass. Self-absorption is not considered in the case of air particulate filters because of the impracticality of accurately weighing the deposit and because the penetration depth of the deposit into the filter is unknown.

Calculation of Samole Activity and 2 Siama Error:

5.p 2 5+S Result , t, ) t,2 ts (pCinf) 2.22($(@(.02832) 2.22($(@(.02832)

Net Activity Counting Error where:

N = total counts from sample (counts) t, = counting time for sample (min)

B = background rate of counter (cpm) t, = counting time for background (min) 2.22 = dpm/pCi v = volume of sample analyzed in cubic feet calculated from l the elapsed time meter l E - efficiency of the counter l 2 = multiple of counting error  !

.02832 = conversion to cubic meters l The MDL is defined as that value equal to the two sigma counting error of the result. I E-7

~

DETERMINATION OF l-131 IN MILK SAMPLES GPUN Environmental Radioactivity Laboratory Stable iodine carrier is equilibrated in a 3.5 liter volume of raw milk before l pumping through 25cc of anion exchange resin to extract iodine. The system is washed with de-ionized water until clear and the washed resin is transferred to a gamma counting container and analyzed by gamma spectroscopy.

Calculation of Samole Activity and 2 Siama Uncertaintv:

l The same calculations are used as in DETERMINATION OF GAMMA I EMITTING RADIOlSOTOPES below.  !

1 E-8 i

1 t

DETERMINATION OF l-131 IN MILK SAMPLES Teledyne Brown Enoineerino  :

i Two liters of sample are first equilibrated with stable lodide carrier. A batch treatment with anion exchange resin is used to remove iodide from the sample. The iodine is then stripped from the resin with sodium hypochlorite, reduced with hydroxylamine hydrochloride, and extracted into carbon tetrachloride as free iodine. It is then back-extracted as iodide into sodium bisulfite solution and is precipitated as palladium iodide. The precipitate is weighed for chemical yield and is mounted on a nylon planchet for low level beta counting. The chemical yield is corrected by measuring the stable iodide content of the milk or water with a specific ion electrode.

Calculation of the Samole Activity and 2 Sioma Error:

$_p 2 5+1 Result , t, y t' to NO (2.22)(v)(E)(p)(exp-A) (2.22)(v)(E)(y)(exp-l)

Net Activity Counting Error where:

N = total counts from sample (counts) t, = counting time for sample (min) 8' = background rate of counter (cpm)

t. = counting time for background (min) 2.22 = dpm/pCi v = volume of sample analyzed (liters) y = chemical yield of the amount of sample counted A = is the radioactive decey constant for 1-131 (0.693/8.05)

At = is the elapsed time between sample collection (or end of  !

the sample collection) to the midcount time 2 = ' multiple of the counting error E - efficiency of the counter for 1-131, corrected for self l absorption effects by the formulai:

E = E* W (exp"*)

E-9

where:

E, = efficiency of the counter determined from an 1-131 standard mount M = mass of Pdl, on the sample mount (mg)

M, = mass of Pdl, on the standard mount (mg)

The MDL is defined as that value equal to the two sigma counting error of the result.

t f

t 2

E - 10 i

~

.Q -

- . - - - - -~ - - _-.. - - . . . . -. __.- - _ _ _ _ _ _ _ -,

DETERMINATION OF GAMMA EMITTING RADIOlSOTOPES GPUN Environmental Radioactivity Laboratory The procedure for detection of gamma emitting radioisotopes generates high resolution gamma spectra which are used for quantitative determination and identification. Standard geometries have been established to maximize efficiency for sample types: air particulate filters, water, milk, soil / sediment i

and food products. l 1

A description of the analytical methods, beginning with air particulates used for each sample type is presented, followed by the general formula used for calculation of the sample activities.

Air particulate: At the end of each calendar quarter,13 (or 14) weekly air filters from the given location are stacked in a two inch diameter Petri dish in chronological order, with the oldest filter at the bottom, nearest the detector, and the newest one on top. The Petri dish is closed and the sample counted.

Water and Milk: A well-mixed 3.5-liter sample is poured into a Marinelli beaker. The samples are brought to ambient temperature and counted.

Soil and Sediment: The sample is dried, sieved and put into a counting container and counted.

Food products: The sample is chopped up and put into a counting container and counted.

Calculation of Sample Activity and 2 Siama Uncertainty: I P. ga r,, AEn A=

2.22xqxexbxE,, (1_,-AEn) where:

A = the computed specific activity P = peak area 2.22 = dpm/picoCuries q = sample quantity E = deteClion efficiency b = gamma-ray abundance Et - elapsed live time A = decay constant E - 11 I

1

Ts = acquisition start time En = elapsed real time

' A P' 2.'AbAs32r ,y ,32(g AA=A hrP, g r b><100 where: AA = uncertainty in the activity A Deosy= A T"" x ' A E" - A (T,+ Eg)-1 Tita s 1 -e -*'" j AP = uncertainty in the peak area P Ab = uncertainty in the S-ray abundance AE = uncertainty in the efficiency sys = systematic Uncertainty estimate ( in %)

A7%= uncertainty in the half-life E - 12

)

DETERMINATION OF GAMMA EMnTING RADIOlSOTOPES Teledyne Brown Enoineerino Gamma emitting radioisotopes are determined with the use of a lithium drifted germanium (GeLi) and high purity germanium detectors with high resolution spectrometry in specific media; such as, air particulate filters, charcoal filters, milk and water. Each sample to be assayed is prepared and counted in standard geometries such as one liter wrap-around Marinelli containers,300 ml or 150 ml bottles, or 2-inch filter paper source geometries.

Samples are counted on large (>55 cc volume) GeLi detectors connected to Nuclear Data 6620 data acquisition and computation systems. All resultant spectra are stored on magnetic tape.

The analysis of each sample consists of calculating the specific activities of all detected radionuclides or the detection limits from a standard list of nuclides.

The GeLi systems are calibrated for each standard geometry using certified radionuclides standards traceable to the National Bureau of Standards.

Gamma Soectroscooy Statistically Sionificant Activity and 2 Siama Error Calculation for the ND6620 and ND6700 Systems:

ActMty , ARE4

• MCAY g

pCi y UVETIME(sec.)*ABN*EFFe0.037*(unit mass)

Unit M CSS Statistically Significant Activity

, gnn , 42

• BKGND + AREA ,

AREA 2 Sigma Counting Error Where: '

AREA = Net Peak Area (from Nuclide Une Activity Report)

BKGND = Compton Background (from Nuclide Line Activity Report DECAY = Decay Correction Factor (from Minimum Detectable Activity Report) (Nuclide Half Life - Collection time to Mid Count time) l E - 13

- .. - . . - - - _ = _ - . -. - . . - . . . . . - -. . _ - . .

LIVE TIME = Elapsed Live Time ( from Header Information)

ABN = Nuclide Abundance (from Nuclide Line Activity Report) i EFF = Detector Efficiency (from Nuclide Line Activity l Report)

O.037 = Conversion Factor (dps to picoCuries) unit mass = Sample weight or volume (from Header information)

Gamma Soectroscopy Statistically Non Sianificant Activity and 2 Siama Erro_r_  !

Calculation for the ND6620 and ND6700 Systems: 4 l

1 Activity , AREA

• DECAY pCi UVETIME(sec.)*ABN*EFF*0.037*(unit mass)

(unit massy Statistically Non Significant Activity I

, gnn , 42

• BKGND + NET , y NET i 2 Sigma Counting Error where:

NET = Net Peak Area (from Minimum Detectable Activity Report)  :

BKGND = Compton Background (from Nuclide Line Activity Report)

DECAY = Decay Correction Factor (from Minimum Detectable  ;

Activity Report) (Nuclide Half Life - Collection time to Mid Count time) i LIVE TIME = Elapsed Uve Time ( from Header Information)

(EFF*B.I) = Efficiency

• Abundance (from Minimum Detectable Activity Report) 0.037 = Conversion Factor (dps to picoCuries)-

unit mass = Sample weight or volume (from Header Information)

E - 14

Gamma Spectroscopy Minimum Detectable Activity Calculation for the ND6620 and ND6700 Systems:

MDA- , 2.83 fBKGR

• DECAY g

pCl y LIVETIME(sec.)e(EFFeB.I.)*0.037*(unit mass) unit mass where:

BKGN = Total Peak Background Area (from Minimum Detectable Activity Report)

DECAY = Decay Correction Factor (from Minimum Detectable Activity Report) (Nuclide Half Life - Collection time to Mid Count time)

LIVE TIME = Elapsed Uve Time ( from Header Information)

(EFF*B.1) = Efficiency

• Abundance (from Minimum Detectable Activity Report) 0.037 = Conversion Factor (dps to picoCuries) unit mass = Sample weight or volume (from Header Information) l E - 15

l ENVIRONMENTAL DOSIMETRY GPUN Environmental Radioactivity Laboratory GPU Nuclear thermoluminescent dosimeters (TLDS) are Panasonic Type 801 AS badges, two of which are deployed at each station. Each badge contains two calcium sulfate and two lithium borate elements. Since each element responds to radiation independently, this provides eight independent detectors at each station. The calcium sulfate elements are shielded with a thin layer of lead, which makes the response to different energies of gama radiation more linear. The lead also shields the calcium sulfate elements from beta radiation, so that they respond to gamma radiation only. The two lithium borate elements are shielded differently to permit the detection of beta radiation.

Only the calcium sulfate elements normally are used for environmental monitoring; however, the lithium borate elements can be used to evaluate beta exposures or as a backup to the calcium sulfate elements should more data be required.

TLDs are annealed and read using a Panasonic UD701 A TLD Reader equipped with glow curve capture capability. A reader alignment is performed monthly using TLDs irradiated to a known exposure. Run Correction Factors (RCF) are inserted in each read batch to correct for small drifts in reader calibration. An Element Correction Factor (ECF)is generated for each element before a new TLD badge is placed into service to standardize each element to a known exposure. The ECF for each element is updated every two years. Each calcium sulfate element is annealed to a total residual exposure of less than 0.5 mR prior to being issued each time that a badge is used.

Control (transit) badges are issued with every batch of field TLDs and accompany the badges into the field to quantify transit exposure. After the field badges are deployed, the control badges are kept in a lead shield with minimum 2" thick lead during the period of field exposure. Additional control badges are kept in a lead shield for the entire quarter, and receive essentially no transit exposure. All control and field badges are read together at the end of each quarter, and the average field control badge exposure is subtracted from the average shield control badge exposure to generate the transit exposure. The transit exposure (generally less than 1 mR total) is subtracted from the gross exposures on the field badges to yield the net exposures. Net exposures are then converted to mR per standard month. This method of calculating transit exposure conforms to guidance contained in ANSI N545.

f E - 16

Each station comprises two TLD badges, each of which has two calcium sulfate elements. Outliers are identified using predefined algorithms. If all four elements are available, a given exposure value is judged an outlier if the standard deviation exceeds 5% of the mean exposure based on all four elements, and the exposure for one element is outside three standard deviations of the mean exposure based on the other three elements. If only two elements are available, the relative standard deviation based on the two exposure values must be 12% or less, or else both exposure values are considered outliers and no valid data are reported for that station for that quarter. ,

l l

l 1

l 1

I E - 17

l I

1 i

i APPENDIX F QUALITY CONTROL EPA INTER-LABORATORY COMPARISON PROGRAM 1

APPENDIX F: QUALITY CONTROL PROGRAM GPU Nuclear (GPU) and Teledyne Brown Engineering (TBE) participate in the EPA Radiological Inter-laboratory Comparison (cross check) Program. This participation includes a number of analyses on various sample media as found in the Peach Bottom Atomic Power Station REMP. As a result of this participation, an objective measurement of analytical precision and accuracy as well as, a bias estimation of the results are obtained.

Examination of the data shows that the vast majority were within the EPA control limits. Each case of exceeding the control limits was investigated. There was no evidence to suggest systematic errors.

The results of GPU's and TBE's participation in the EPA cross check program can be found in Table F-1.

i F-1 6

TABLE F-1 USEPA INTER-LABORATORY COMPARISONS - 1995 GPU NUCLEAR AND TELEDYNE BROWN ENGINEERING Collection Media Nuclide EPA Results GPU Nuclear - ERL Teledyne Brown Date (a) Results (b) Engineering Results(b) 01/13/95 Water Sr-89 20.0 8.7 -

(c) 19.00 i 2.65 Sr-90 15.0 1 8.7 -

(c) 14.00 1 0.00 01/27/95 Water Gr Alpha 5.0 1 8.7 -

(d) 5.00 i 1.00 Gr-Beta 5.0 t 8.7 -

(d) 6.00 1.00 02/03/95 Water 1-131 100.0 17.3 100 t 2.52 88.33 i 2.31 (e) 03/10/95 Water H-3 7435.0 i 1290.8 -

(f) 7066.67 i 115.47 04/18/95 Water Gr-Alpha 47.5 i 20.6 31.67 i 3.21 39.67 i 2.52 Gr-Beta 86.6 i 17.3 75.00 i 2.00 80.33 i 2.52 Sr-89 20.0 i 8.7 -

(c) 20.67 i 1.15 Sr-90 15.0 1 8.7 -

(c) 14.67 i 0.58 Co-60 29.0 i 8.7 29.67 i 0.58 31.67 i 2.08 Cs-134 20.0 i 8.7 18.67 i 0.58 19.67 1 1,73 Cs-137 11.0 1 8.7 10.00 i 1.00 11.67 1 1.53 06/09/95 Water Co-60 40.0 1 8.7 40.33 i 1.53 42.33 i 2.52 Zn-65 76.0 i 13.9 76.00 1 5.57 82.33 i 3.51 Cs-134 50.0 i 8.7 46.00 i 1.73 46.67 i 2.08 Cs-137 35.0 1 8.7 35.00 i 2.65 37.67 1 1.15 Ba-133 79.0 i 13.9 79.67 1 2.08 74.33 i 2.08 07/14/95 Water Sr-89 20.0 1 8.7 -

(c) 18.33 i 1.53 Sr-90 8.0 i 8.7 -

(c) 8.00 i 0.00 7/21/95 Water Gr-Alpha 27.5 i 12.0 28.33 i 4.04 18.33 1 1.53 (g)

Gr Beta 19.4 i 8.7 20.67 i 3.51 19.33 i 1.53 08/04/95 Water H-3 4872.0 1 844.9 4933.33 i 57.74 4866.67 i 152.75 8/25/95 Air Filters Gr-Alpha 25.0 1 10.9 25.00 1 1.73 23.67 i 1.53 Gr-Beta 86.6 i 17.3 76.67 i 2.89 84.67 i 1.53 Sr-90 30.0 1 8.7 -

(c) 25.33 i 0.58 Cs 137 25.0 i 8.7 28.00 i 0.00 27.00 i 1.00 09/29/95 Mik Sr-89 20.0 1 8.7 -

(c) 23.33 i 3.06 Sr-90 15.0 t 8.7 -

(c) 16.33 1 0.58 l131 99.0 i 17.3 98.33 i 1.53 103.33 t 5.77 Cs-137 50.0 i 8.7 51.33 i 2.89 54.67

• 2.52 Total K 1654.0 i 144.0 1733.33 i 57.74 1683.33 i 136.50 F-2

TABLE F-1 USEPA INTER-LABORATORY COMPARISONS - 1995 GPU NUCLEAR AND TELEDYNE BROWN ENGINEERING Collection Media Nuclide EPA Results GPU Nuclear ERL Telodyne Brown Date (a) Results (b) Engineering Results(b) 10/06/95 Water I-131 148.0 1 26.0 156.67 5.77 150.0 t 0.00 10/17/95 Water Gr-Alpha 99.4 i 43.1 103.33 i 5.77 94.67 i 6.00 .

Gr-Beta 141.8 i 36.9 120.00 i 10.00 120.00 i 10.00 I Co-60 49.0 i 8.7 49.33 i 2.08 53.33 1 5.37 Sr-89 20.0 8.7 -

(c) 20.67 i 3.00 Sr-90 10.0 i 8.7 -

(c) 9.30 i 1.20 Cs-134 40.0 8.7 33.33 i 0.58 34.37 i 4.03 Cs 137 30.0 8.7 29.00 i 1.73 35.10 i 3.93 10/27/95 . Water Gr-Alpha 51.2 i 22.2 32.00 i 0.00 37.00 1 3.00 Gr-Bata 24.8 i 8.7 28.67 t 1.53 25.33 i 1.53 19/03/95 Water Co-60 60.0 i 8.7 57.33 3.79 58.00 i 7.00 Zn-65 125.0 i 22.6 133.33 i 5.77 131.33 i 19.14 l Ba-133 99.0 1 17.3 94.67 i 1.53 91.33 i 3.06 l Cs-134 40.0 i 8.7 85.67 1 2.31 36.33 1 2.08 Cs 137 49.0 i 8.7 49.33 i 1.53 50.33 i 4.62 Footnotes:

(a) EPA ResuRs - Expected laboratory precision (control limit i 3 sigma). Units are pCL/ liter for water and mik except K is in mg/ liter. Units are total pCl for air particulate filters.

(b) Results - Average one sigma. Units are pCi/ liter for water and mik except K is in mg/Itter. Units are total pCi for air particulate filters.

(c) No data available. Analysis not performed by laboratory.

(d) The ERL results were not reported to the EPA. The sample was analyzed six times and the precision of the individual resuRs was not acceptable. The ERL policy is to report only highly confident resuRs and since the confidence level could not be achieved from this sample the results were not submitted to the EPA.

(e) The normalized deviation marginally exceeded the waming level and an apparent trend in the resuRs appeared. The cause was a probable high bias in the beta counting efficiency. Check source control charts did not indicate any changes in the counting equipment, so the 1-131 calibration was suspected.

New l 131 calibrations were performed July 3 through 6,1995 after receiving a new standard from the EPA.

The intercomparison sample data sheets were recalculated with the new efficiencies and the average resut F-3

was in excellent agreement with the EPA (96 pCi/l versus the EPA value of 100 pCi/I). The discrepancy in the 1131 efficiency between the current calibration and the previous one (aside from the uncertainty in the standard) appears to be an abnormally low yield in the preparation of the standard for the older calibration which created a high bias in the counter efficiencies. The bias was less than ten percent, therefore further corrective action or revision of previously reported data is deemed not necessary.

(f) The ERL tritium results were not reported to the EPA in time for the report. The ERL result (average 3 determinations) was 7533.33 i 208.17 pCi/1. The value was within all limits (0.23 sigma of known). Also, the precision (R.A. - 0.318) was acceptable.

(g) The mineral salt content of the water used by the EPA to prepare the samples has been shown to vary substantially throughout the year. Absorption curves to account for mount weight may vary from the true absorption characteristics of a specific sample. Previous results do not indicate a trend toward "out of control" for gross alpha / beta analysis and the normalized deviation from the grand average is only -0.36.

The normalized deviation from the known for TBE-ES does not exceed three standard deviations and intemal spikes have been in control. No corrective action is planned at this time.

F-4 vr

I

(

l i

s I

! APPENDIX G i, .

i l f 1

! PBAPS SURVEY  :

i l-1 3

d i

4

APPENDIX G: PBAPS SURVEYS

' A Land Use Census around the Peach Bottom Atomic Power Station (PBAPS) was condacted by Normandeau Associates, RMC Environmental Services Division for PECO Energy to comply with Section 3.8.E.2 of PBAPS's Offsite Dose Calculation Manual Specifications (ODCMS) and Bases. The survey was conducted during the May to October 1995 growing season. The distance and direction of all locations were positioned from the barn to the PBAPS vents using Global Positioning System (GPB) technology. The results of this survey are summarized in Table G-1.

The farm identified in the WSW sector had a calculated D/O that was 20 percent greater than an existing farm in the program. This farm has been added to the 1996 REMP.

• 9 r

O G-1

'.1

TABLE G-1 LOCATION OF THE NEAREST MILK PRODUCING ANIMAL WITHIN A FIVE MILE RADIUS OF PBAPS,1995 Distance (ft.)

Sector from Vents N 14,995 NNE 11,683 NE 11,897 ENE 11,673 E 15,802 ESE 16,442 SE 25,604 SSE -

S -

SSW 7,324 SW 11,608 WSW 3,995 W 4,576 WNW 9,040 NW 17,570 NNW -

- lNDICATES NO MILK ANIMALS LOCATED G-2

_ _ _ . _ _ _ _ _ _ _ _ _ _ _ _ -