ML20078G555
| ML20078G555 | |
| Person / Time | |
|---|---|
| Site: | Peach Bottom  |
| Issue date: | 05/31/1983 |
| From: | RADIATION MANAGEMENT CORP. (RMC) |
| To: | |
| Shared Package | |
| ML20078G554 | List: |
| References | |
| NUDOCS 8310120316 | |
| Download: ML20078G555 (121) | |
Text
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PEACH BOTTOM ATOMIC POWER STATION 1
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L Regional Radiological Environmental Monitoring Program L
Report #18
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January 1,1982 Through December 31,1982 L
Prepared For PHILADELPHIA ELECTRIC COMPANY By
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RADIATION MANAGEMENT CORPORATION University City Science Center 3508 Market Street q
Philadelphia, Pa.19104 g
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8310120316 830922 PDR ADOCK 05000277 R
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PEACH BOTTOM ATOMIC POWER STATION L
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Regional Radiological Environmental Monitoring Program Report #18 January 1, 1982 Through December 31, 1982
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Prepared For k
PHILADELPHIA ELECTRIC COMPANY By
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RADIATION MANAGEMENT CORPORATION f
L University City Science Center 3508 Market Street Philadelphia, PA 19104
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May 1983
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TABLE OF CONTENTS PAGE I.
SUMMARY
AND CONCLUSIONS 1
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INTRODUCTION A.
Program Objectives 3
B.
Program implementation 4
li1.
RMC PROGRAM DESCRIPTION
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A.
Sampie ColIeciIon & TLD P1acement 5
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B.
Program Changes 7
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C.
Analyses Performed 7
D.
Exceptions to the Program 7
IV.
RESULTS AND DISCUSSION r
A.
Data Interpretation & Statistical 9
i Analysis B.
Discussion of Results 10 1.
Surface Water 10 2.
Discharge Water 11 3.
Well Water 12 L
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Precipitation 13 5.
Air Particulates 13 6.
Air lodine 14
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7.
Milk 14 8.
Soli 15 9.
Ambient Gamma Radiation 16 V.
TABLES VI.
FIGURES Vll.
SYNOPSIS OF ANALYTICAL PROCEDURES VIII.
EPA lNTERLABORATORY COMPARISON PROGRAM
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LIST OF TABLES TABLES 1.
RMC Station Designation and Sample identification System for Peach Bottom Atomic Power Station REMP, 1982 11.
RMC Sample Collection and Analysis Program
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Summary of Analyses Performed on Samples Collected During i
1982 IV.
Summary of Radioactivity Concentrations in Samples Collected j
in the V!cinity of Peach Bottom Atomic Power Station, 1982 j
V.
Summary of Gamma Spectrometry of Samples Collected in the i
Vicinity of Peach Bottom Atomic Station, 1982 VI.
Summary of Ambient Cosimetry Program Vll.
Analytical Data for Surf ace Water Grab Samples
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Vill.
Analytical Data for Surface Water Composite Samples IX.
Concentrations of Gamma Emitters in Surf ace Water-in the Vicinity of Peach Bottom Atomic Power Station,1982 X.
Analytical Data for Discharge Water Grab Samples XI.
Analytical Data for Discharge Water Composite Samples X!l.
Concentrations of Gamma Emitters in Discharge Water in the Vicinity of Peach Bottom Atomic Power Station,1982 Xill.
Analytical Data for Well Water Samples XIV.
Analytical Data for Precipitation Samples XV.
Concentrations of Ganwna Emitters in Precipitation in the Vicinity of Peach Bottom Atomic Power Station,1982 XVI.
Analytical Data for Air Particulate Samples XVil.
Concentrations of Gamma Emitters in Air Particulates in the Vicinity of Peach Bottom Atomic Power Station, 1982 XVill.
Concentrations of I-131 in Filtered Air in the Vicinity of Peach Bottom Atomic Power Station, 1982 XIX.
Concentrations of I-131 and Tritium in Milk in the Vicinity of Peach Bottom Atomic Power Station,1982 4
XX.
Weekly Mean Concentrations of I-131 in Milk in the Vicinity q
of Peach Bottom Atomic Power Stgtlon,1982 j
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LIST OF TABLES (CONT.)
TABLES
'XXI.
Concentrations of Sr-89, Sr-90 and Gamma Emitters in Milk in the Vicinity of Peach Bottom Atomic Power Station,1982
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XXil.
Concentrations of Sr-89, Sr-90 and Gamma Emitters in Soll in the Vicinity of Peach Bottom Atomic Power Station, 1982
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XXill.
Monthly TLD Results XXIV.
Quarterly TLD Results f
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Mean Monthly and Quarterly TLD Results for the Site Boundary, Middle and Outer Rings
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XXVI.
Typical Minimum Detectable Levels of Nuclides Searched for but not found in the Vicinity of Peach Bottom Atomic Power Station, 1982
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LIST OF FIGURES FIGURE 1
Environmental SamptIng Stations on or near Peach Bottom Site 2
Environmental Sampling Stations at Intermediate Distances from Peach Bottom Site
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3 Environmental SampiIng Stations at Remote Distances from
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Peach Bottom Site 4
Comparison of Monthly Aqueous Tritium Concentrations in Surf ace Water Collected Near Peach Bottom Atomic Power Station, 1982 (Total Sample-Composite) 5 Comparison of Quarteriy Aqueous Tritium Concentrations In Surface Water Collected Near Peach Bottom Atomic Power Station, 1982 (Total Sample-Composite) 6 Comparison of Monthly Gross Beta Concentrations in Surf ace Water Collected near Peach Bottom Atomic Power Station, 1982 (Soluble Fraction-Grab) 7 Comparison of Monthly Gross Beta Concentrations in Surf ace Water Collected Near Peach Bottom Atomic Power Station,1982 (Insoluble Fraction-Grab) 8 Comparison of Monthly Aqueous Tritium Concentrations in Surface and Discharge Water Collected Near Peach Bottom Atomic Power Station,1982 (Total Sample-Composite)
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9 Comparison of Monthly Gross Beta Concentrations in Surf ace and Discharge Water Collected Near Peach Bottom Atomic Power Station,
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1982 (Soluble Fraction-Composite) 10 Comparison of Monthiy Gross Beta Concentrattons in Surf ace and 1
Discharge Water Collected Near Peach Bottom Atomic Power Station, J
1982 (Insoluble Frc.ction-Composite)
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11 Comparison of Average Aqueous Tritium Concentrations in Well Water Collected Near Peach Bottom Atomic Power Station,1970-1982 (Total Sample-Grab) 12 Comparison of Average lodint-131 Concentrations in Milk at Near, Intermediate and Distant Farms in the Vicinity of Peach Bottom Atomic Power Station,1982 (Total Sample)
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13 Comparison of Average Strontium-90 Concentrations in Soli Collected Near Peach Bottom Atomic Power Station, 1970-1982 1
(Top one Inch)
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f LIST OF FIGURES (CONT.)
FIGURE 14 Comparison of Average Strontium-90 Concentrations in Soil Collected Near Peach Bottom Atomic Power Station, 1 7 0-1982 (Bottom Cut) 15 Comparison of Average Cesium-137 Concentrations in Soll Collected Near Peach Bottom Atomic Power Station, 1970-1982 (Top one Inch) 16 Comparison of Average Cesium-137 Concentrations in Soll Collected Near Peach Bottom Atomic Power Station, 1970-1982 (Bottom Cut) g
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17 Comparison of Average Monthly TLD Results Collected at Site l
Boundary, Middle and Outer Ring Stations in the Vicinity of Peach Bottom Atomic Power Station, 1982 18 Comparison of Average Quarterly TLD Results Collected at the Site l
Boundary, Middle and Outer Ring Stations in the Vicinity of Peach Bottom Atomic Power Station, 1973-1982
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SUMMARY
AND CONCLUSIONS r
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SUMMARY
AND CONCLUSIONS This report on the radiological environmental monitoring program con-ducted at the Peach Bottom Atomic Power Station for Philadelphia Electric Company by Radiation Management Corporation covers the period January 1, 1982 to December 31, 1982. During this period 4613 analy-ses were performed on 3971 samples.
Surface water and discharge water samples were analyzed for concentra-tions of tritium, gross beta, and gamma-emitting nuclIdes.
Surface water was also analyzed for concentrations of gross alpha. Compari-sons of unaf fected stations with potentially af fected stations, in Conowingo Pond, showed no significant difference in concentrations of the radionuclides studied.
It was shown that no significant differ-ences existed between the preoperational and operational periods; therefore, it ca1 be concluded that the levels of radioactivity in Conowingo Pond wster have not been measurably influenced by the operation of the Peach Bottom Atomic Power Station.
High sensitivity.-131 analyses wsre performed on weekly air samples.
All results were is:s than the minimum detectable level.
High sensitivity 1-13' analyses were also performed on weekly milk samples while cows were on pasture and on monthly samples when cows were not grazing. All results were less than the minimum detectable level.
Soll samples were analyzed for concentrations of Sr-89, Sr-90 and gamma-emitting nuclides and levels observed were not significantly different from preoperational data.
Environmental gamma radiation measurements were made using thermolumi-nescent dosimeters.
Results from the site-boundary, middle and outer rings were found to be not significantly different, so it can be con-l cluded that the operation of Peach Bottom Atomic Power Station did not
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produce measurable levels of ambient gamma radiation at any of f-site location.
In assessing alI the data gathered for this report and comparing the results with preoperational data, it was evident that the operution of the Peach Bottom Atomic Power Station resulted in no significant radiological impact on the environment.
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II.
INTRODUCTION
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INTRODUCTION Radiation Management Corporation (kMC) began conducting a radiologi-cal environmental monitoring program in September 1970 for the Phila-delphia Electric Company in connection with the Peach Bottom Atomic Power Station (PBAPS) located in Peach Bottom Township, York County, Pennsylvania. This RMC program complements an existing program being conducted by others which has been carried out since March 1%0.
PBAPS is located along the Susquehanna River between Holtwood and Conowingo Dams. The fourteen mile long pond created by Conowingo Dam is called Conowingo Pond.
The initial loading of fuel into Peach Bottom Unit #1, a 40 MWe (Net) 1 high temperature gas-cooled reactor, was started on February 5,1%6, and initial criticality was achieved March 3, 1966. Final shutdown of Peach Bottom Unit #1 was on October 31, 1974. Peach Bottom Unit #2 and #3 are boiling water reactors each with a power output of approxi-mately 1050 MWe (Net). The first fuel was loaded into Unit #2 on August 9,1973, and criticality was first achieved on September 16, 1973. The fuel was loaded into Unit #3 on July 5, 1974 and criticali-ty was first achieved on August 7, 1974. Peach Bottom Unit #2 first reached full power on June 16, 1974. Peach Eottom Unit #3 first reached fulI power on December 21, 1974.
Results of the RMC portion of the overall regional radiological environmental monitoring program have been reported in semi-annual reports. Semi-annual reports were discontinued af ter 1975. This report contains data for samples representing the period January 1, 1982 through December 31, 1982.
A special preoperational report (1) for Peach Bottom Units #2 and #3 has been issued previously which summarizes results of all analyses
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performed by RMC on samples collected from the start of the RMC por-tion of the overall program through August 8, 1973, the day before fuel was first loaded into Peach Bottom Unit #2.
r A.
PROGRAM OBJECTIVES
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1.
Identify, measure, and evaluate existing radionuclides in the environs of the Peach Bottom Site and any fluctuations in radioactivity levels which may occur.
2.
Monitor and evaluate ambient radiation levels.
3.
Determine, within the scope of the program, any measurable quan-tity of radioactivity introduced to the environment by the opera-tion of the Peach Bottom Atomic Power Station.
4.
Complement other existing radiological environmental monitoring programs at Peach Bottom Atomic Power Station, t
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B.
PROGRAM IMPLEMENTATION in order to achieve these objectives, Radiation Management Corporation performed the following analyses on samples collected during the period of this report.
1.
Measured and evaluated concentrations of aqueous tritium in surf ace sater, discharge water, well water and milk.
2.
Measured and evaluated concentrations of alpha emitters in surface water.
3.
Measured and evaluated concentrations of beta emitters in surface water, discharge water, well water, precipitation and air particulates.
4.
Identified, measured and evaluated gamma emitting radionuclides in surface water, discharge water, precipitation, air particu-lates, milk and soll.
5.
Measured and evaluated concentrations of I-131 in milk, air and surface water.
6.
Measured and evaluated concentrations of Sr-89 and Sr-90 in soll and milk.
7.
Measured ambient gamma radiation levels in the environment and evaluated the variations with time and location with respect to the Site.
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I III.
RMC PROGRN4 DESCRIPTION M
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RMC PROGRAM DESCRIPT10N A.
SAMPLE COLLECTION AND TLD PLACEMENT PROCEDURES The program being conducted by RMC is described in Tables I and iI and Figures 1-3.
1.
Sample Collection a.
Water (except precipitation)
All samples were collected in new polyethylene bottles. All
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persons involved in sample collection and handling were ad-vised not to wear tritium luminous dial watches in order to avoid possible cross contamination from that source.
Sample containers were rinsed at laast twice with the water to be sampled before collection.
All water samples were grab samples except those collected at stations ILL, IMM, 61 and 4L.
Weekly samples were taken from a tank which continually collects a sample at these four locations.
The weekly samples were composited into a monthly samplo for analysis.
Collection methods are de-scribed in more detail in Table 11,Section V.
I b.
Precipitation Precipitation was collected in ar. apperatus consisting of a new polyethylene bottle with a plastic funnel 8 inches in e
diameter. The bottle was replaced monthly and the sample l
bottle was shipped to RMC for analysis. The amount of pre-cipitation was recorded continuously by a separate rain gauge at station IA.
c.
Air Particulates f
Air particulate samples were obtained using a vacuum sampler H
and glass fiber filters, approximately 2" in diameter. The filter was replaced weekly and sent to RMC for analysis.
r The vacuum sampler was run continuously at approximately 1 l
cubic foot per minute.
d.
Air lodine 1
Air Iodine samples were obtained using a vacuum sampler and charcoal filters, approximately 2" in diameter. The filter was replaced weekly and sent to RMC for analysis. Tha vacuum sampler was run continuously at approximately I cubic foot per minute.
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Milk Milk samples were coilected in new polyethylene bottle from the bulk tank at each farm, refrigerated and shipped immedi-ately. No preservative was added.
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Soll Soll samples consisting of seven cores, 2" in diameter and 6" deep were collected f rom a 50 X 50 f t. area at each sam-pling location. Top soll (upper 1 inch) and bottom soll (lower 5 inches) were separated, then sealed in separate plastic bags, and shipped to RMC.
2.
TLD Placement A system using thermoluminescent dosimeters (TLDs) was used to measure the direct radiation levels in the PBAPS environment.
The TLD stations were placed on and around the Peach Bottom Site using the "three ring concept". Two on-site stations, designated as plant omnplex stations are not included in any of the three rings.
a.
A site boundary ring near and within the site perimeter, representing fencepost doses, i.e., at locations where the doses are greater than maxitnum annual off-site doses from Station releases; b.
A middle ring extending to approximately 10 miles from the Site, designed to measure possible exposures to close-in l
population; c.
An outer ring extending f rom approximately 10 to about 60 miles from the Site; and considered not to be affected by Station releases; d.
The specific location of each station was determined by the following criteria:
(1) The presence of relatively densely populated areas; (2) From 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 the Station, if any, would be more significant; (3) On hills and (where practical) within sight of the stack, and free from local obstructions; (4) Near the closest house to the stack in the prevailing down-wind direction, e.
Each TLD set (4 TLDs por set) was placed in a sealed poly-ethylene package to verify the integrity of the dosimeters when collected.
Two packages were kept in a locked formica
" birdhouse" or polyethylene jar, about six feet above the ground or supporting surface at each location. At each station one package was exchanged for measurement on a monthly schedule, and one on a quarterly schedule.
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PROGRAM CHANGES f
None C.
ANALYSES PERFORMED The schedule of analyses performed by RMC is listed by sample g
type in Table 11.
This schedule was followed except where noted 1
below. Table lll lists the type and number of analyses performed during this period by sample type and station location. Methods used in performing these analyses can be found in Section Vil of L
this report.
D.
EXCEPTIONS TO THE PROGRAM 1.
Discharge water samples were not collected from station IMM from q
1/08/82 to 1/15/82 and 5/21/82 to 5/28/82 due to pump malf unc-tions.
2.
1-131 data were not available for surface water samples collected f rom stations 4L and 61 f rom 11/27/82 to 12/04/82 due to a computer malfunction.
3.
TLD data were unavailable from station 46 for October,1982 due to vandalism.
4.
Milk sample from station A collected 6/28/82 was unavailable for analysis due to shipping loss.
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IV. RESULTS AND DISCUSSION f
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f IV. RESULTS AND DISCUSSION A.
DATA INTERPRETATION AND STATISTICAL ANALYSIS Several factors are important in the interpretation of the data.
In order to avoid undue repetition in the discussion which fol-lows, these factors are described below.
1.
Grab SampiIng
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Grab sampling is a useful and acceptable procedure for taking environmental samples of a medium in which the con-centration of radionuclides is expected to vary slowly with
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time or where intermittent sampling is deemed sufficient to establish the radiological characteristics of the medium.
This method, however, is only representative of the sampled
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medium for that specific location and instant of time. As L.
a result, variation in the radionuclide concentrations of the samples wilI normally occur.
Since these variations will tend to counterbalance one another, the extraction of averages based upon repetitive grab samples is va!Id.
2.
Minimum Detectable Levels (MDL)
It is characteristic of environmental monitoring data that many results occur at or below the specified detection level.
Formal statistical error analysis of groups of such data is difficult. Pragmatic approaches to the problem in-clude counting the detection level entries as zero, as half the detection level value, or as full detection level value.
For reporting and calculation of averages in this report, any result occurring.at or below the minimum detectable level is considered to be at that level.
Averages obtained
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using this method are therefore biased high.
3.
Standard Deviation of Analytical Results E
Within the data tables an approximate 95% (2 sigma) confi-dence interval is supplled for those data points at and
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above the minimum detectable level. These Intervals repre-L sent the range of values into which 95% of repeated counts of the prepared sample would fall.
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Table Means and Standard Deviations Results for each type of sample were grouped according to the analysis performed.
Means and standard deviations of these results were calculated. These standard deviations represent the variability of measured results for different I
samples rather than single analysis uncertainty.
For these calculations, all results below the MDL were considered to be at the MDL. As a result, the means are biased high, and d
the standard deviations are biased low.
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B.
DISCUSSION OF RESULTS Results are summarized in brief form in Tables IV, V and VI (Section V).
Tablos of results for individual sample types and analyses performed can be found in Section V, Tables Vil to XXVI. Graphical presentations of results can be found I.
Section VI.
1.
Surface Water Samples were taken from eight stations on a monthly sche-dule. Three stations (ILL, 4L and 61) were continuous com-posite samples and f ive (1Q, 4F, 4G, 6A and 13A) were grab i
samples.
Station 13B was sampled a total of eight times in 1982. Of these stations, seven could be af fected by re-leases from Peach Bottom Atomic Power Station. The re-maining stations (6A and 61) were above Holtwood Dam and, therefore, could not be af fected by plant discharges (re-fer to Figures 1 and 2,Section VI, for station locations).
The fol lowing analyses were performed on surf ace water sam-ples.
a.
Tritium Total samples from seven stations were analyzed for con-centrations of aqueous tritium.
Samples from stations ILL, 1Q, 4L and 61 were analyzed on a monthly basis, while
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samples from stations 4F, 6A and 13A were composited monthly into a quarterly sample.
Results of this analysis for surf ace water samples can be found in Tables Vil and Vill,Section V.
The concentrations detected were within the range found during the Peach Bottom Units #2 and #3 preoperational period (1).
Graphical comparisons of the unaf fected stations (6A and 61) above Holtwood Dam with potentially affected stations (4F and 4L) at Cono-wingo Dam showed no detectable addition of tritium to Conowingo Pond from the operation of PBAPS (Figures 4 and 5,Section VI).
b.
Gross Alpha Samples f rom four stations (4F, 4L, 6A and 61) were analyzed for gross alpha concentrations in tho soluble and insoluble fractions. Results of gross alpha anal-ysis in surface water samples can be found in TaDles Vil and Vill,Section V.
Results at all locations were generally at or below tha minimum detectable level in the soluble fraction. Results of the insoluble fraction Indicated a small amount of activity present.
Most activity levels found were within the range of the MDL values observed.
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Gross Beta Samples from all stations, were analyzed for concentrations of gross beta in the soluble and insoluble fractions.
Re-suits of gross beta analysis in surface water samples can be found in Tables Vll and Vlli,Section V.
The concentra-tions detected in the soluble fraction were within the range observed during the preoperational period for Units #2 and and #3 (1).
Detectable activities were observed in the in-soluble fraction of surface water.
The activities observed f
were within the range of the MDL values. A graphical comparison of two Conowingo Dam stations (4F and 4G) with one Holtwood Dam station (6A) showed the results of the
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soluble and insoluble fractions to be generally the same for all three locations (Figures 6 and 7,Section VI).
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d.
iodine-131 Samples collected during the last week of each month from 1/09/82 to 12/04/82 from two stations (4L and 61) were anal-yzed for concentrations of I-131.
Results of I-131 analysis of surf ace water samples can be found in Table Vill,Section V.
Most results were below the minimum detectable level.
f Detectable concentrations were found at station 4L in Febru-ary, and at station 61 in March. The 1-131 activity was attributed to upstream sources.
e.
Gamma Spectrometry r
Samples from alI stations were analyzed for gamma-emitting
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nuclides by gamma spectrometry.
Results of gamma spectro-metry on surface water samples can be found in Table IX, e
Section V.
The nuclides searched for were below the mini-L mum detectable level with the exception of K-40 which was found at two stations, 61 and 138.
2.
Discharge Water Sanples were taken from two stations (IM and IMM) on a monthly schedule (refer to Figure 1,Section VI, for L
station locations). The following analyses were performed on discharge water samples.
a.
Tritium Total samples from both stations were analyzed for concen-(
trations of aqueous tritium on a monthly basis.
Results of tritium analysis in discharge water samples can be found in Table X and XI,Section V.
The concentrations detected s
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were within the range found during the Peach Bottom Units
- 2 and #3 preoperational period (1).
A graphical compari-son of concentrations of aqueous tritium results for com-posite surface water and discharge water samples showed no significant differences (Figure 8, Sectin VI).
b.
Gross Beta Monthly samples from both stations were analyzed for gross beta concentrations in the soluble and insoluble fractions.
Results of these analyses in discharge water samples can be found in Tables X and X:,Section V.
The concentrations detected in the soluble and insoluble fractions were simi-lar to those observed in surface water samples (Figures 9 and 10,Section VI).
c.
Gamma Spectromotry Samples from both stations were analyzed for gamma-emitting nuclides by spectrometry. Results of gamma spectrometric analysis are given in Table XI1,Section V.
AlI nuclIdes were less than the minimum detectable level.
3.
Well Water Samples were taken from four stations on a quarterly sche-dule. Two stations (1U and IV) were located within the Site area. The other stations were located approximately one mile (station 40) and 10 miles (station 7) from the Plant. These station locations are shown in Figures 1 and 2,Section VI.
The following analyscs were performed on welI water samples.
a.
Tritium Total samples from ai! four stations were analyzed for aqueous tritium concentrations.
Results of tritium anal-ysis of well water samples can be found in Table Xill,Section V.
Results of all samples were within the range found during the Peach Bottom Units #2 and #3 preopera-tional period (1).
A graphical comparison of the distant site-area, and on-site wells showed that tritium le is have been gradually decreasing with time due to the a sa-tion of routine atmospheric nuclear weapons testing (Figure 11,Section VI).
b.
Gross Beta Samples from all four stations were analyzed for gross beta concentrations in the soluble and insoluble fractions.
Re-suits of gross beta analysis on well water samples can be found in Table Xill,Section V.
The concentrations detec-ted in the soluble fraction were within the range observed 12
l during the Peach Bottom Units #2 and #3 preoperational period (1). Concentrations detected in the insoluble frac-tion were similar to data observed for surface and discharge water.
4.
Precipitation 4
Precipitation was collected f rom two stations on a monthly schedule.
Station IA is located at the on-site Peach Bottom Weather Station #1.
Station 8, located in Colora, f
MD., is approximately 10 miles from the Site (for station locations, refer to Figures 1 and 2,Section VI). The fol-lowing analyses were performed on precipitation samples.
a.
Gross Beta
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Monthly samples were analyzed for gross beta concentrations in the total sample.
Results of gross beta analysis in precipitation samples can be found in Table XIV,Section V.
Concentrations detected were within the range found during
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the Peach Bottom Units #2 and #3 preoperational period (1).
b.
Gamma Spectrometry Monthly samples were analyzed for gamma-emitting nuct ides by spectrometry of the total sample. Results of gamma spec-
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trometric analysis of samples from both stations are given in Table XV,Section V.
Be-7 was found in two of twenty-four samples and can be attributed to cosmic ray activity.
5.
Air Particulates Continuous air particulate samples were collected from the r
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on-site Peach Bottom Weather Station #1 (1Z) and from the intermediate location, Conowingo Dam (4A) (For station locations, see Figure 1 and 2, section VI). The following analyses were performed on air particulate samples, a.
Gross Beta Weekly samples were analyzed for concentrations of beta emmitters. Results of gross bete analysis of air particu-(
late samples can be found in Table XVI,Section V.
Results
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observed were similiar to levels observed in previous years.
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b.
Gamma Spectrometry Monthly composite samples were analy:cd for gamma-emitting nuclides by gamma spectrometry.
Results of gamma spectro-metric analysis are given in Table XVil,Section V.
Be-7 was detected in 22 of 24 samples and was the result of cosmic ray activity.
Naturally occuring K-40 was found in 5 of 24 samples. Co-60 was found at the on-site station 1Z in July with an activity of 611 pCI/m3. Confirmation was made by recount analysis.
6.
Air lodine Continuous air samples were collected at eight stations and analyzed weekly for 1-131.
Three stations (18,1Z, 2) were located within the Site area.
Four stations (3A, 5, 6B, 14) were located at Intermediate distances of 1.9 to 5.8 miles from the site.
One station (12D) was located 62 miles from the Site. Results of I-131 analysis can be found in Table XVill,Section V.
All results of the 416 analyses performed were less than the minimum detectable level.
7.
Milk Milk was sampled at eleven f arms; three f arms (G, J and 0) located within two miles of PBAPS were designated "near farms"; four farms (D, L, M and N) located 3 to 5 miles from PBAPS were designated as " Intermediate farms"; and four farms (A, B, C and E) located greater than five miles from PBAPS were designated as " distant f arms".
The following analyses were performed on milk samples.
a.
Tritium Milk from four farms (A, C, G and J) was analyzed for tri-tium concentrations in the aqueous fraction on a quarterly basis. Results of tritium determinations in milk samples s
can be found in Table XIX,Section V.
Concentrations de-tected were within the range found during the Peach Bottom Units #2 and #3 preoperational period (1).
b.
lodine-131 Milk from eight farms (A, B, C, D, G, J, N and 0) near Peach Bottom was analyzed for concentrations of I-131, monthly in January, February, March and December. Weekly 1-131 analy-ses resumed during the last week of March and continued 14 l
f through the fourth week of November. Three additional farms (L, M and E) were sampled and analyzed quarterly for 1-131.
Results of I-131 analysis can be found in Tables XIX and XX,
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Section V and Figure 12,Section VI.
All results were less I
than the minimum detectable level.
c.
Strontium-89 and Strontium-90 One milk sample was collected at farm J in each quarter and analyzed for Sr-89 and Sr-90.
Results can be found in Table f
XXI,Section V.
Except for the third quarter which had a result of 6+3 pCi/l, Sr-89 results were less than the minimum detectable level.
Sr-90 concentrations were similar to those
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observed in previous years.
d.
Gamma Spectrometry One milk sample collected at f arra J in each quarter was analyzed for gamma-emitting nuct ides by gamma spectrometry.
Results can be found in Table XXI,Section V.
Nuclides de-(
tected were naturally occurrng K-40 and Cs-137. Cesium-137 is commonly found in rallk as a result of world-wide f allout.
(
8.
Soll Semiannual samples were taken at three locations, one on-site station (2) and two distant stations (3A and 5) located
{
about four miles from PBAPS (for station locations, see Figures 1 and 2,Section VI). The area at station 2 is heavily wooded with rock outcroppings. The soll at this location would be expected to contain substantial humus from the accumulation of natural vegetative debris.
Station 3A is covered only with grass.
Station 5 is a combination of
(
grass and cultivated land. The following analyses were per-formed on soll samples.
(
a.
Strontium-89 and Strontium-90 Samples from alI stations were analyzed for Sr-89 and Sr-90 concentrations in the top one inch and bottom five inches
[
separately.
Results of Sr-89 and Sr-90 analysis in soll samples can be found in Table XXil,Section V.
Concentr a-tions of Sr-89 were less than the minimum detectable f
level in all samples. Concentrations of Sr-90 detected were within the range found during the PBAPS Units #2 and #3 pre-operational period (1).
Graphical comparisons of Sr-90 in
(
the top one Inch and bottom cut can be found in Figures 13 and 14,Section VI.
Dif ferences between the on-site location (2) and distant locations (3A and 5) were attributed to the
{
accumulation of vegetative debris at station 2.
[
[
15
b.
Gamma Spectrometry l
Samples from all stations were analyzed for gamma-emitting l
nuclides oy Ge(LI) gamma spectrometry (Table XXil,Section V).
Nuclides identified were generally the same as those found during the PBAPS Units #2 and #3 preoperational period with most at the same or lower concentrations (1).
Some naturally-occurring nucIldes were found (K-40, Ra-226, Th-232). Small concentrations of Cs-137 were detected in
(
all twelve samples and were similiar to levels observed in 1
l previous years. The 30 year half-life and biological assimilation of Cs-137 accounts for the continued appearance of this nuclide in soll samples many years after atmospheric testing of nuclear weapons. Dif ferences between the on-site location (2) and distant locations (3A and 5) were attribu-ted to the accumulation of vegetative debris at station 2 (Figures 15 and 16,Section VI). Sb-125, a Plant produced nuclide, was observed at the detection level at the on-site station 2.
9.
Ambient Gamma Radiation Ambient gamma radiation levels were measured with calcium sulfate: Tm thermoluminescent dosimeters.
l Thirteen stations (1B,10,1D, IE,1F,1G,1H, IJ, IL, IM, 1NN, 2 and 40) were located around the Sito boundary and designated for comparison purposes as the " sit'e boundary ring".
Twenty-five stations (3A, 4K, 5, 6B, 14, 15, 17, 22, 23, 26, 27, 31, 32, 33A, 38, 42, 43, 44, 45, 46, 47, 48, 49, 50 and 51) were located within u 10 mile radius of the Site and designated as the " middle ring".
Seven sta-tions (12B,16,18,19, 20, 21B and 24) were located f rom 10 to 60 miles from the Site and designated as the " outer ring".
Since they could be more directly affected by Plant activities and do not represent doses to the public, t A stations (1A and 11) located within the plant complex con-stitute a fourth group called plant-complex stations (fcr station locations, see Figures 1, 2 and 3,Section VI).
Results of TLD measurements are Iisted in Tables XXII 1, XXIV and XXV,Section V.
The annual average of monthly and quarterly radiation levels were within the range found during the Peach Bottom Units #2 and #3 prooperational period (1).
Graphical comparisons of the site-boundary, middle and outer rings on monthly and quarterly readings showed no sign-Ificant differences in ambient radiation levels with distance from PBAPS, Indicating no measurabla Station contribution (Table XXV,Section V, Figures 17 and 18,Section VI).
1 16
L REFERENCES '
f f
(1)
Radiation Management Corporation Publication, Peach Bottom haLC fagel-Station Preonerational Radiological Monitoring Reno-t. tan Units R and H, January 1974, Philadelphia, Pa.
(2)
Interex Corporation, Peach Bottom Atomic Power Station l
Regional.Egylrgng Radiation Monitoring Program Precoerational l
Summary Reoort, Units R and H, Februarv 2, M through August H,1911, June 1977, Natick Mass.
(3)
Radiation Management Corporation, " Quality Control Data - 1982 Annual Report," March, 1983.
s e
h V
I L
17
4 d
- O a-aA hA M 4e4_S u4 a4, shr.,A, 4,,
a,,,a,,
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a,,
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i
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i V.
TABLES
(
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f
TABLE I RMC STATION DESIGNATION AND SAMPLE IDENTIFICATION SYSTEM FOR PEACH BOTTOM ATOMIC POWER STATION REMP. 1982 VV-WWW-XXYZ General code for identification of samples, where:
11-Power Plant identification code PB Peach Bottom Atomic Power Station
)GfM Type of Sample f
SWA - Surface Water DWA Discharge Water WWA WelI Water
{
RWA Rain Water APT Air Particulates f
A10 Air lodine MLK Milk r
l' SOL Soll
[
IDM immersion Dose L
XX Angular Sector of Sampiing Location I
L Compass is divided into 36 sectors of 10 degrees each with center at Peach Bottom off-gas stack.
Sector 36 is centered r
due North, and others are numbered in a clockwise direction.
Sector 00 is used to designate an unidentified direction.
1
- Radial Zone of Sampling Location (in this report, the Radial distance from the Peach Bottom off-gas stack for all regional stations).
S:
on-site location D:
3-4 miles off-site n
A:
0-1 mile off-site E:
4-5 miles off-site B:
1-2 miles off-site F:
5-10 miles off-site J
C:
2-3 miles off-site G:
10-20 miles off-site L
H:
20-100 miles off-site Station's Numerical Designation within sector and zone, using Z
r 1,2,3.... In each sector and zone.
g I
L r
L e
- _ - = _ -.
TfGLE II Ri1C SA!!PLE COLLECTION AND ANALYSIS PROGRAM ENV.
STATION LOCATION STATION RMC STATION DIRECTION & DISTANCE COLLECTION tETHOD ANALYSIS AND FREQUENCY NO.
STATION NAf1E DESIGNATION FROM PEACH BOTTOM
& FREQUENCY PERFORMED A.
SURFACE WATER ILL Peach Bottom PB-SWA-6S4 Continuous sampler Water is continuously sampled Tritium - Monthly Units 2&3 On Site at Units 2&3 Intake from the Peach Bottom Units Gross Beta (S+I) - Monthly Intake - Composite 1200' ENE of Units 2 & 3 2&3 Intake and is collected Gama Spec - Monthly in a 190 gallon tank. Each i
week 2 4ts. are withdrawn l
from the tank prior to drain-l ing the tank and placed in a 2 gallon polyethylene bottle to form a monthly co@osite sa@le.
l IQ Peach Bottom PB-SWA-653 On Site at Unit #2 Intake Two gallon grab sa@le is Same as station ILL above l
Unit #2 about 1200' ENE of Units 283 collected in front of intake Intake structure monthly.
4F Conowingo Dam PB-SWA-14F2 Ir. the Conowingo Hydro-Two gallon grab sa@le is Tritium - quarterly comp.
El. 33' electric Station, 3.6 taken monthly from the same Gross Alpha (S+I) - monthly MSL miles SE of Units 2 & 3.
header which is used for the Gross Beta (S+I) - monthly composite sa@le (4L). This Gama Spec - monthly header continuously draws pond water from about elevation 33' I1SL. This sa@le and PB-SWA-14F3 sa@les are collected at the same time.
4G Conowingo Dam PB-SWA-14F3 At Conowingo Dam in Two gallon grab sample is Gross Beta (S+I) - monthly Surface flaryland, 0.5 miles SE collected near the surface Gama Spec - monthly of Units 2&3. Water sa@le of the Pond on the upstream is taken from Conowingo side of the dam monthly.
Pond on upstream side of dam.
4L Conowir.go Dam PB-SWA-14F5 Continuous sampler in Water is continuously sa@ led Tritium - monthly El. 33' MSL -
Conowingo Hydroelectric from a header which draws Pond Gross Alpha (S+1) - monthly Co @osite Station; about 8.6 miles water from elevation 33' itSL Gross Beta (S+I) - monthly SE of Units 2 & 3.
and is collected in a 175 gal.
Gama Spec - monthly tank. Each week 2 qts, are withdrawn from the tank prior to draining the tank and placed in a 2 gal polyethylene bottle l
to form a monthly co @ osite sample.
6A Holtwood Dam PB-SWA-33F1 At Holtwood Dam, Pa.,
Two gallon grab sample is col-Same as station 4F above Hydroelectric 5.8 miles NW of Units 2&3.
lected from Holtwood Pond at Station Hydroelectric Station iatake
- monthly,
~
~
~
m_a
m m
m m
TABLE II(cont.)
RMC SAMPLE COLLECTION AND ANALYSIS PROGRAfi ENV.
STATION LOCATION STATION RMC STATION DIRECTION & DISTANCE COLLECTION METHOD ANALYSIS AND FREQUENCY NO.
STATION NAFE DESIGNATION FRON PEACH BOTTOM
& FREQUENCY PERFORMED 6I Holtwood Dam PB-SWA-33F4 Continuous sampler at Water is continuously Tritiura - monthly Hydruelectric Holtwood Dam, Pa., 5.8 sa@ led from the Holtwood Gross Alpha (S+I) - monthly Station-Composite miles NW of Units 2 & 3.
Hydroelectric Station Gross Beta (S+I) - monthly Intake and is collected in Gama Spec - monthly a 175 gal. tank. Each week 2 qts, are withdrawn from the tank prior to draining the tank and placed in a 2 gal. polyethylene bottle to form a monthly composite l
sa mle.
13A Chester Water PB-SWA-11C1 On east shore of Conowingo Two gallon grab sa mle Tritium - quarterly comp.
Intake-Pond Pond at Chester Water is collected from Conowingo Gross Beta (S+I) - rnonthly Authority Intake 2.4 Pond near the shore monthly.
Gamma Spec - monthly miles ESE of Units 2 & 3.
13B Chester Water PB-SWA-11C2 At Chester Water Authority Two gallon grab sample is Gross Beta (S+I) - monthly Intake-pu@
Intake. The same as collected from purnp discharge Gansna Spec - monthly Discharge PB-SW-11C1 but the sample during any month that the
{
is collected from the pu@
pu@ operates.
discharge.
B.
DISCHARGE WATER IM Peach Bottom PB-DWA-1352 Located at Canal Discharge Two gallon grab sa@le is Tritium - monthly Canal Discharge structure; 1.0 miles SE collected at the exit of Gruss Beta (S+I) - monthly of Units 2 & 3.
the discharge canal monthly.
Ganina Spec - monthly 1791 Peach Bottom PB-DWA-1355 A continuous sampler Water is continuously sampled Same as station 1!! above Canal -
on site at canal discharge from the Peach Bottom Unit Discharge -
1.0 miles SE of Units 2 & 3.
283 discharge canal and is col-Co@osite lected in a 190 gallon tank. Each week 2 qts. are withdrawn from the tank prior to drain-ing the tank and placed in a 2 gal. polyethylene bottle to form a monthly co@osite sample.
- - - - - _. -. ~...
TABLE II (cont.)
Rl1C SAf1PLE COLLECTION AND ANALYSIS PROGRAF 1 ENV.
STATION LOCATION STATION R:1C STATION DIRECTION a DISTANCE COLLECTION !!ETHOD ANALYSIS AND FREQUENCY-
]
NO.
STATION NAME DESIGNATION FROM PEACH BOTT0!!
-A FREQUENCY PERF0iD1ED 3
C.
WELL WATER IU Peach Bottom PB-WA-ISS2 Well at Plant Site. 140'1' Well pump is run for Tritium - quarterly Si te-Utili ty
~ S of Units 2 & 3.
several minutes prior to Gross Beta (S+I) quarterly Building sampling in order to flush the sample line. Then two gallon grab sample is j
taken from the building i
faucet quarterly.
t i
IV Peach Bottom PB-WA-1252 Well at Plant Site. 1400' Same as station IU above Same as station IU above Site-Info.
SSE of Units ? & 3.
o j
Center j
7 Darli ngton, !!d.
PB-WA-16F1 9.6 miles SSE of Units 2 & 3 Same as station IU above Same as station IU above Area in llarford Co., !!d.
40 Peach Bottom PB-WA-21B2 Well in Site Area,1.5 miles Same as station IU above Same as station IU above Site Area SW of Units 2 & 3.
D.
PRECIPITATION 1A Peach Bottom' PB-RWA-11S1 On Site at Weather Station The sample from the rain Gross Beta - monthly Weather
- 1, 0.3 miles SE of Units collector is shipped to Gama Spec - monthly Station #1 2 a 3.
RT1C monthly. The rain collector consists of an 8-inch dianeter plastic funnel connected to a two-gallon polyethylene contai ner.
8 Colora, tid.
PR-Rt/A-12F1 9.9 miles ESE of Units 2 & 3 Same as station IA above Same as station IA above-in Cecil, Co., !!d.
E.
AIR PARTICULATES - AIR IODINE 10 Peach Bottom PB-AIO-3351 On Site, 0.3 miles SE of About 1 cfm continuous flow I-131 - weekly Weather Station Units 2 & 3.
through charcoal filter
- 2 (approx. 2" diam.) is in-stalled for a week and re-pl aced.
IZ Peach Bottom PB-APT-1154 On Site at Weather Station About I cfm continuous flow Gross Beta - weekly Weather Station
- 1, 0.3 miles SE of L' nits 2 & 3.
through glass fiber and char-I-131 - weekly
- 1 coal filters (approx. 2" Gamma Spec - monthly comp.
diam.) are installed for a week and replaced.
n w
v n
TABLE II (cont.)
R!1C SA!1PLE COLLECTION AND ANALYSIS PROGRAM -
ENV.
STATION LOCATION STATION R1C STATION DIRECTION & DISTANCE COLLECTION !!ETH00 ANALYSI', AllD FREQUENCY
. NO.
STATION NAME DESIGNATION FR0!! PEACH BOTT0!i a FREQUENCY.
PERFORMED E.
AIR PARTICULATES - AIR IODINE (cont.)
2 Peach Bottom PB-AID-1351 On Site,0.9 miles SE of Same as station IB above I-131 - weekly Site 130* Sector Units 2 a 3.
Hill 3A Delta, Pa.
PB-AID-23D1 3.6 miles S!! of Units 2 & 3 Same as station 18 above I-131 - weekly.
Substation at Delta, Pa.
4A Conowingo Dam PB-AID-14F1 8.6 miles SE of Units 2 & 3 About I cfm continuous flow Gross Beta - weekly Powerhouse mof on Powerhouse roof in Cecil through a glass fiber filter Gama Spec - monthly comp.
County, tid.
(approx. 2" diam.) is installed for a week and replaced.
S Wakefield, Pa.
PB-AIO-8E1 At Wakefield, Pa., 4.6 miles Same a station IB above I-131 - weekly E of Units 2 & 3.
6B Holtwood Dam PR-AIO-33F2 On the roof of Hydroelectric Same as station 18 above 1-131 - weekly Hydmelectric Station, 5.8 miles IM of Units Station of Units 2 & 3.
14 Peters Cmek PB-AIO-1081 1.9 miles ESE of Units 2 & 3 Same as station 18 above I-131 - weekly near mouth of Peters Creek 12D Phila., Pa.
PB-AIO-8H2 62 miles ENE of Units 2 & 3 Same as station 10 above I-131 - weekly 2301 !1arket St.
on the mof of 2301 !1arket Street.
F.
MILK Regional PB-!L K-12 F1 Distant regional fams Two gallon grab sample I-131 weekly Fam A surrounding the Site, is collected at each Aq tritium - quarter!y designated "A", "B" and fam from a tank containing Regional PB-!LK-24F1 "C" on the west side of milk from all cows weekly I-131 - weekly Fam B Conowingo Pond and "E" while cows are on pasture, on the east side of monthly othemise.
Conowingo Pond. Nearby Samples are shipped to R!iC.
Regional PB-!LK-31F1 mgional fam surrounding Same as station A above Farm C the Peach Bottom Site on the west side of Conowingo Regional PB-!1LK-5D1 Pond are designated "G", "J".
Same as station B above Fam D
TABLE II (cont.)
RMC SAMPLE COLLECTION AND ANALYSIS PROGRAM ENV.
STATION LOCATION-STATION RMC STATION DIRECTION & DISTANCE
' COLLECTION METHOD ANALYSIS AND FREQUENCY NO.
STATION NAMC DESIGNATION FR0fi PEACH BOTTOM
& FREQUENCY PERFORMED F.
MILK (cont.)
Regional PB-MLK-36F1 and "0".
Regional fams Same as station A above I-131 - quarterly Farm E at intermediate distances except quarterly from Peach Bottcm on the Regional PB-MLK-20B1 east side are designated Same as station A above Farm G "0",
"L", "H" and "N".
Regional PB-MLK-28A1 I-131 - weekly Farn J Aq tritium - quarterly Sr-89 & quarterly Gamma Spec - quarterly Regional PB-MLK-581 Same as station A above I-131 - quarterly Fam L except quarterly Regional PB-M.K-7C1 Same as station A above Same as station L above Farm M except quarterly Regional PB-MLK-11C3 Same as station B above Farm N Regional PB-MLK N C1 Same as station B above Farm 0 G. SOIL 2
Peach Bottom PB-50L-1351 On Site, 0.9 miles SE Seven cores (2" in diameter Gama Spec-semiannual 130' Sector of Units 2 & 3.
and 6" deep) are collected Sr-89 & semiannual Hill from a 50 X 50 ft. area semi-annually. Top 1 inch and bottom 5 inches are separated, sealed in plastic bags, and shipped to RMC.
3A Delta, Pa.
PB-50L-23D1 3.6 miles SW of Units 2 & 3 Same as station 2 above Same as station 2 above Substation at Del ta, Pa.
5 Wakefield, Pa.
PB-50L-8E1 4.6 miles E of Units 2 & 3 Same as station 2 above Same as station 2.above at Wakefield, Pa.
m
m TABLE II(cont.)
Rl1C SAMPLE COLLECTION AND ANALYSIS PROGRAM ENV.
STATION LOCATION STATION RMC STATICN DIRECTION & DISTANCE COLLECTION t1ETHOD ANALYSIS AND FPIQUENCY NO.
STATION NAME DESIGNATION FR0!! PEACH BOTTOM
& FREQUENCY PERFORMED H.
ENVIRONMENTAL DOSIMETRY - TLD At each of the following stations there are 2 environmental dosimeter packets with 4 TLDs per package.
One packet is replaced monthly, and one quarterly. The packets for each time period am collected and replaced on the same day at all the stations.
IA Peach Bottom PB-IDM-11S1 On Site, 0.3 miles SE of Procedure for collection TLD - monthly & quarterly Weather Units 2 & 3.
is described in the Station #1 placement procedure in Sec. II., A.
IB Peach Bottom PR-IDM-3351 On Site,0.5 miles IM of TLD - monthly & quarterly i
Weather Units 2 & 3.
Station #2 IC Peach Bottom PB-IDM-16S1 On Site, 0.9 miles SSE of TLD - monthly & quarterly South Units 2 & 3.
Substation Rd.
1D Peach Bottom PB-IDM-14S1 On Site,0.7 miles SE of
- TLD - monthly & quarterly 140* Sector Units 2 & 3.
Site Boundary 1E Peach Bottom PB-IDM-3551 On Site, 0.6 miles NtM of TLD - monthly & quarterly 350' Sector Units 2 & 3.
Site Boundary IF Peach Bottom PB-IDH-20S1 On Site, 0.6 miles SSW of TLD - monthly & quarterly 200* Sector Units 2 & 3.
Hill 1G Peach Bottom PB-IDH-30S1 On Site, 0.7 miles WIM of TLD - monthly & quarterly North Units 2 & 3.
Substation 1H Peach Bottom PB-IDf1-27S1 On Site, 0.6 miles W of TLD - month'.y & quarterly Site 270*
Units 2 & 3.
Sector Hill II Peach Bottom PB-IDil-15S1 On Site, 0.6 miles SSE of TLD - monthly & quarterly South Units 2 & 3.
Substation IJ Peach Bottom PR-IDH-1851 On Site, 0.7 miles S of TLD - monthly & quarterly Site 180*
Units 2 & 3.
Sector Hill
=
_. _ =.
TABLE II(cont.).
RMC SAMPLE COLLECTION AND ANALYSIS PROGRAM ENV.
STATION LOCATION STATION Rf1C STATION
. DIRECTION & DISTANCE COLLECTION MET 110D ANALYSIS AND FPIQUENCY NO.
STATION NAME DESIGNATION FROM PEACH BOTTOM
& FREQUENCY PERFORMED H.-
ENVIRONMENTAL DOSIMETRY - TLD (cont.)
1L Peach Bottom PB-IDM-652 Located near Unit 3 TLD - monthly & quarterly Unit J
. Intake structure; 0.2 miles Intake ENE of Units 2 & 3.
IM Peach Bottom PB-IDM-13S2 Located near Canal Discharge TLD - monthly & quarterly Canal Discharge structure; 1.0 miles SE of Units 2 & 3.
INN Peach Bottom PR-IDM-26S1 On Site, 0.5 miles WSW of TLD - monthly & quarterly Site Units 2 & 3.
2 Peach Bottom PB-I!X1-1351 On Site, 0.9 miles SE of TLD - monthly & quarterly Site 130*
Units 2 & 3.
L Sector Hill 3A Delta, Pa.
PB-IDM-23D1 3.6 miles SW of Units 2 & 3.
TLD - monthly & quarterly Substation 4K Conowingo Dam PB-IDM-14F1 On roof of Conowingo Power-TLD - monthly & quarterly Powe rhouse house, 8.6 miles SE of Units Roof 2 & 3.
I 5
Wakefield, Pa.
PB-I DM-BE1 At Wakefield, Pa. 4.6 miles TLD - monthly & quarterly E of Units 2 & 3.
6B Holtwood Dam PB-IDM-33F2 On roof of Hydroelectric TLD - monthly & quarterly Hydroelectric Station, 5.B miles IM of Station Units 2 & 3.
128 Phila., Pa.
PR-IDM-BH1 On roof of Radiation TLD - monthly & quarterly 3508 Market St.
Management Corp., Philadelphia, Pa., 64 miles E of Units 2 & 3.
14 Peters Creek PR-IDM-1081
'1.9 miles ESE of Units 2 & 3 near TLD - monthly & quarterly the Mouth of Peters Creek g
15 Silver Spring PB-IDM-36D1 3.6 miles N of Units 2 & 3 near TLD - monthly & quarterly Road Sil /er Spring Road 16 Nottingham, Pa.
PB-10M-9G1 12.8 niles E of Units 2 & 3 at TLD - monthly & quarterly Substation Nottingham Substation.
_s m --
u
c-.,
c-,
,~,
TABL5 II(cont.)
RMC SAMPLE COLLECTION AND ANALYSIS PROGRAM ENV.
STATION LOCATION STATION R!1C STATION DIRECTION & DISTANCE COLLECTION METHOD ANALYSIS AND FREQUENCY NO.
STATION NAME DESIGNATION FR0!1 PEACH BOTTOM
& FREQUENCY PERFORMED H.
ENVIRONMENTAL 00SIMETRY - TLD (cont.)
17 Riverview PB-IDft-11El 4.0 miles ESE of Units 2 & 3 TLD - monthly & quarterly I
Road near Riverview Road.
18 Fawn Gmve, Pa.
PB-IDM-26 F1 10 miles W of Units 2 & 3 at TLD - monthly & quarterly Fawn Gmve. Pa.
19 Red Lion, Pa.
PR-IDM-30H1 20.6 miles WiM of Units 2 & 3 TLD - monthly & quarterly at 9ed Lion Pa.
20 Bel Air, Md.
PB-IDM-20G1 15.1 miles SSW of Units 2 & 3 RD - monthly & quarterly Area near Bel Air, Maryland.
21B Lancaster, Pa.
PB-IDft-35G1 19 miles NfM of Units 2 & 3 TLD - monthly & quarterly Area near Lancaster, Pa.
22 Eagle Road PB-IDM-3C1 2.4 mile'. NNE of Units 2 & 3 TLD - monthly & quarterly near Eagle Road.
23 Peach Bottom PB-IDM-15B1 Off-site Hill 1.0 miles TLD - monthly & quarterly 150* Sector Hill SSE of Units 2 & 3.
Off Site 24 Harrisville Md.
PB-IDM-11G1 10.9 miles ESE of Units 2 & 3 TLD - monthly & quarterly Substation at Harris Substation 26 Slab Road PB-IDM-31El 4.2 miles IM of Units 2 & 3 TLD - monthly & quarterly near Slab Road.
J 27 N. Cooper PB-IDM-18C1 2.6 miles S of Units 2 & 3 TLD - monthly & quarterly Road near H. Cooper Road.
31 Pilotown PB-IDM-13E1 4.9 miles SE of Units 2 & 3 TLD - monthly & quarterly Road near Pilotown Road.
32 Slate Hill PB-I D!t-6 C1 2.7 miles ENE of Units 2 & 3 TLD - monthly & quarterly Road near Slate Hill Road.
33A Fulton Main PB-IDH-6B2 1.7 miles ENE of Units 2 & 3.
TLD - monthly & quarterly Weather Station 38 Peach Bottom PB-IDH-801 3.0 miles E of Units 2 & 3 TLD - monthly & quarterly Road near Peach Bottom Road.
n TABLE II(cont.)
R;1C SAMPLE COLLECTION AND ANALYSIS PROGRAft ENV.
STATION LOCATION STATION Rl1C STATION DIRECTION & DISTANCE COLLECTION !!ETHOD ANALYSIS AND FREQUENCY.
NO.
STATION NAME DESIGNATION FR0:1 PEACH BOTT0:1 A FRE UENCY PERFOR!ED H.
ENVIRONMENTAL DOSIMETRY - TLD (cont.)
40 Peach Bottom PB-ID!1-21B2 In Site Area about 1.2 miles TLD - monthly & quarterly Site Area SW of Units 2 & 3.
42 Muddy Run PB-IDM-35El 4.2 miles NNW of Units 2 & 3.
TLD - monthly & quarterly Environmeatal Lab 43 Drumore Township PB-IDit-2F1 5.0 miles NNE of Units 2 & 3.
. TLD - monthly & quarterly School 44 Coshen Mill PB-IDM-5F1 5.1 miles NE of Units 2 & 3.
TLD - monthly & quarterly
- Road 45 PB - Keeney Line PB-IDf1-7D1 3.3 miles ENE of Units 2 & 3.
TLD - mnthly & quarterly 46 Broad Creek PB-IDl1-16El 4.5 miles SSE of Units 2 & 3 TLD - monthly & quarterly near F11ntville Road.
47 Broad Creek PB-IDri-18E1 4.3 miles S of Units 2 & 3.
TLD - monthly & quarterly Scout Camp 48 Macton Substation PB-IDM-20E1 5.0 miles SSW of Units 2 f. 3 TLD - monthly & quarterly 49 PB-Conastone Line PB-ICH-F5 El 4.1 miles WSW of Units 2 & 3.
TLD - monthly & quarterly 50 TRANSCO Punping PB-IDH-26El 4.9 miles W of Units 2 & 3.
TLD - monthly & quarterly Station 51 Fin Substation PB-IDM-29D1 4.0 miles WNW of Units 2 & 3.
TLD - monthly & quarterly
{
I
. ~-
~
w
m
~,
TABLE III
SUMMARY
OF ANALYSES PERFORMED ON SAMPLES COLLECTED DURING 1982 l
Type of Analysis l
Station RMC Number of Gross Gross Gamma Total No.
Designation Location Samples H-3 Beta Alpha TLD Spec.
SURFACE WATER l
IQ PB-SW-6S3 Peach Bottom 12 12 24 12 48 Unit #2 Intake -
l Grab ILL PB-SW-6S4 Peach Bottom 12 12 24 12 48 Unit #2 & 3 Intake -
Composite 13A PB-SW-llc 1 Chester Water 12 4
24 12 40 Intake Pond 13B PB-SW-llc 2 Chester Water Intake -
8 16 8
24 Pump Discharge 4F PB-SW-14F2 Conowingo Dam 12 4
24 24 12 64 El 33' MSL-Grab 4G PB-SW-14F3 Conowingo Dam 12 24 12 36 i
Surface-Grab
)
4L PB-SW-14F5 Conowingo Dam 12 12 24 24 12 11 83 El 33' - Composite 6A PB-SW-33F1 Holtwood Dam 12 4
24 24 12 64 Hydroelectric Station 61 PB-SW-33F4 Holtwood Dam 12 12 24 24 12 11 83 Hydroelectric Station
TABLE III (continued)
SUMMARY
OF ANALYSES PERFORMED ON SAMPLES COLLECTED DURING 1982 Type of Analysis Station RMC Number of Gross Gross Gamma Total No.
Designation Location Samples H-3 Beta Alpha TLD Spec.
B.
DISCHARGE WATER IM PB-DW-13S2 Peach Bottom 12 12 24 12 48 Canal Discharge-Grab IMM PB-DW-13SS Peach Bottom 12 12 24 12 48 Canal Discharge -
Composite C.
WELL WATER IU PB-WW-15S2 Peach Bottom Site 4
4 8
12 Utility Bldg.
l IV PB-WW-12S2 Peach Bottom Site 4
4 8
12 l
Info. Center 40 PB-WW-21B2 Peach Bottom 4
4 8
12 Site Area I
7 PB-WW-16F1 Darlington, MD Area 4
4 8
12 l
l D.
AIR IODINE AND PARTICULATES IB PB-AIO-33S1 Peach Bottom 52 52 52 Weather Station #2 IZ PB-AP-liS4 Peach Bottom 52 52 12 52 116 Weather Station #1 2
PB-AIO-13S1 Peach Bottom Site 52 52 52 130' Sector Hill m___m u-w-
v
n n
e n,
n TABLE III (continued)
SUMMARY
OF ANALYSES PERFORMED ON SAMPLES COLLECTED DURING 1982
)
i Type of Analysis Station RMC Number of Gross Gross Gamma Total No.
Designation Location Samples H-3 Beta Alpha TLD Spec.
AIR IODINE AND PARTICULATES (continued) 3A PB-AIO-23D1 Delta, PA 52 52 52 Substation 4A PB-AP-14F Conowingo Dam 52 52 12 64.
Powertouse Roof 5
PB-AIO-8El Wakefield, PA 52 52 52 6B PB-AIO-33F2 Holtwood Dam 52 52 52 Hydroelectric Station 14 PB-AIO-10Cl Peters Creek 52 52 52 12D PB-AIO-8H2 Phila., PA 52 52 52 2301 Market St.
E.
RAIN WATER 1A PB-RW-IISI Peach Bottom 12 12 12 24 Weather Station #1 8
PB-RW-12F1 Colo ra, MD 12 12 12 24 F.
MILK PB-M-24F1 Regional Farm A 38 4
38 42 PB-M-19G1 Regional Farm B 38 38 38
TABLE III (continued)
SUMMARY
OF ANALYSES PERFORMED ON SAMPLES COLLECTED DURING 1982 Type of Analysis Station RMC Number of
-Gross Gross Gamma Total No.
Designation Location Samples H-3 Beta Alpha TLD Spec.
MILK (continued)
PB-M-31F1 Regional Farm C 38 4
38 42 PB-M-5DI Regional Farm D 38 38 38 PB-M-36F1 Regional Farm E 4
4 4
PB-M-20B1 Regional Farm G 38 4
38 42 PB-M-28A1 Regional Farm J 38 4
4 38 4
4 54 PB-M-5B1 Regional Farm L 4
4 4
PB-M-7C1 Regional Farm M 4
4 4
PB-M-11C3 Regional Farm N 38 38 38 PB-M-22C1 Regional Farm 0 38 38 38 G.
SOIL 2
PB-E-13S1 Peach Bottom 4
4 4
4 12 130' Sector Hill 3A PB-E-23D1 Delta, PA 4
4 4
4 12 Substation 5
PB-E-8El Wakefield, PA 4
4 4
4 12
+__s
- u u
w m
TABLE III (continued)
SUMMARY
OF ANALYSES PERFORMED ON SAMPLES COLLECTED DURING 1982 Type of Analysis Statior.
RMC Number of Gross Gross Gamma Total No.
Designation Location Samples H-3 Beta Alpha TLD Spec.
ENVIRONMENTAL DOSIMETRY 1A PB-1D-11S1
. Peach Bottom 64 64 64 Weather Station #1 IB PB-ID-33S1 Peach Bottom 64 64 64 Weather Station #2 1C PB-ID-16S1 Peach Bottom 64 64 64 South Substation Road ID PB-ID-14S1 Peach Bottom 64 64 64 140* Sector Site Boundary 1E PB-ID-35S1 Peach Bottom 64 64 64 350* Sector Site Bounda ry IF PB-ID-20S1 Peach Bottom 64 64 64 200* Sector Hill 1G PB-ID-30S1 Peach Bottom 64 64 64 North Substation 1H PB-ID-27S1 Peach Bottom 64 64 64 270* Sector Hill II PB-ID-15S1 Peach Bottom 64 64 64 South Substation IJ PB-ID-18S1 Peach Bottom 64 64 64 180* Sector Hill
TABLE III (continued)
SUMMARY
OF ANALYSES PERFORMED ON SAMPLES COLLECTED DURING 1982 Type of Analysis Station RMC Number of Gross Gross Gamma Total No.
Designation Location Samples H-3 Beta.
Alpha TLD Spec.
ENVIRONMENTAL DOSIMETRY (continued)
IL PB-ID-6S2 Peach Bottom 64 64 64 Units 2 & 3 Intake 1M PB-ID-13S2 Peach Bottom 64 64 64 Canal-Discharge INN PB-ID-26S1 Peach Bottom Site 64 64 64 2
PB-ID-13S1 Peach Bottom 64 64 64 130' Sector Hill 3A PB-ID-23D1 Delta, PA Substation 64 64 64 4K PB-ID-14F1 Conowingo Dam 64 64 64 Powerhouse Roof 5
PB-ID-8El Wakefield, PA 64 64 64 6B PB-ID-33F2 Holtwood Dam 64 64 64 Hydroelectric Station 12B PB-ID-8H1 Phila., PA 64 64 64 3508 Market Street 14 PB-ID-10Cl Peters Creek 64 64 64 15 PB-ID-36D1 Silver Spring Rd.
64 64 64 16 PB-ID-9G1 Nottingham, PA 64 64 64 Substation 17 PB-ID-11El Riverview Rd.
64 64 64 o
w
m r- - +
c,
c..
TABLE III (continu:d)
SUMMARY
OF ANALYSES PERFORMED ON SAMPLES COLLECTED DURING 1982 Type of Analysis Station RMC Number of Gross Gross Gamma Total
]
No.
Designation Location Samples H-3 Beta Alpha TLD Spec.
1-131 Sr-89 Sr-90 Analyses i
H.
ENVIRONMENTAL DOSIMETRY (continued) i 18 PB-ID-26F1 Fawn Grove, PA 64 64 64 19 PB-ID-30G1 Red Lion, PA 64 64 64 20 PB-ID-20G1 Bel Air, MD Area 64 64 64 21B PB-ID-35G1 Lancaster, PA 64 64 64 22 PB-ID-3C1 Eagle Road 64 64 64 23 PB-ID-15B1 Off-site 150' 64 64 64 j
Sector Hill j
24 PB-ID-11G1 Harrisville, MD 64 64 64 26 PB-ID-31El Slab Road 64 64 64 27 PB-ID-18C1 N. Cooper Road 64 64 64 1
31 PB-ID-13F1 Pilotown Road 64 64 64 32 PB-ID-6Cl Slate Hill Road 64 64 64 33A PB-ID-6B2 Fulton Weather 64 64 64 Station 38 PB-ID-8D1 Peach Bottom Road 64 64 64 40 PB-ID-21B2 Peach Bottom Site Area 64 64 64 l
42 PB-ID-35El Muddy Run 64 64 64 Environmental Lab I
l
,i TABLE III (continued)
SUMMARY
OF ANALYSES PERFORMED ON SAMPLES COLLECTED DURING 1982
_ Type of Analysis Station RMC Number of Gross Gross Gamma Total No.
Designation Location Samples H-3 Beta Alpha TLD Spec.
I _131 Sr-89 Sr-90 Analyses H.
ENVIRONMENTAL DOSIMETRY (continued) l 43 PB-ID-2F1 Drumore Township 64 64 64
)
School 44 PB-ID-5F1 Goshen Mill Road 64 64 64 45 PB-ID-7D1 PB-Keeney Line 64 64 64 46 PB-ID-16D1 Broad Creek 63 63 63 47 PB-ID-18E1 Broad Creek 64 64 64 Scout Camp 48 PB-ID-20El Macton Substation 64 64 64 49 PB-ID-25D1 PB-Conastone Line 64 64 64 50 PB-ID-26El TRANSCO Pumping 64 64 64 l
51 PB-ID-29D1 Fin Substation 64 64 64 i
f TOTAL 3971 116 416 96 3007 192 754 16 16 4613 t
t i
w a
va w
w
_m m
TABLE IV SUPNARY OF RADIOACTIVITY CONCENTRATIONS IN SAWLES COLLECTED IN THE VICINITY OF PEACH BOTTOM ATOMIC POWER STATION,1982 No. of Sample Type and Samples Number Period
- Period
- Period **
Pre-op***
tocation Analvsts Analvred Detected Minimum Maximum Mean Mean Units SURFACE WATER Potsntially Aqueous Tritium (Grab) 20 4
<60 160170 81157.
3201250.
pCI/I Affected Aqueous Tritium (Grab-Quarter 1y 8
1
<70 150170 80157 pCI/l Stations Comp.)
(1Q, 4F, Aqueous Tritium (Composite) 24 3
<60.
100170 73122 240130 pCI/I 4G, 13 A-Grab )
Gross Beta (Soluble-Grab) 48 48
.91 4 5.01 6 1.911.2 3.312.6 pCI/I (1LL & 4L)
Gross Beta (Soluble-Composite) 24 24 1.11 4 2.81 5 1.8.5 3.512.6 pCI/I
-Composite)
Gross Beta (Insoluble-Grab) 48 38
<20 240140 54180 pCI/g (4r & 13A)
Gross Beta 24 21
<20 140130 49180 pCl/g
- Quarterly,
( I nsol ubl e-Composi te)
Composite for Gross A1pha (Solubie-Grab) 12 2
<.3 1.51.7
.61.6 pCl/I Tritium)
Gross Alpha (Soluble-Composite) 12 1
<.3 2.41.9
.711.1 pCI/l Gross Alpha (Insoluble-Grab) 12 8
<9 30120 16118 pCi/g Gross Alpha (Insoluble-Composite) 12 5
<10 70 20 24156 pCi/g Unaffected Aqueous Tritium (Grab-Quarterly 4
0
<70
<70
<70 pCi/l Stations Comp.)
(6A-Grab)
Aqueous Tritium (Composite) 12 2
<60 100170 73121 pCI/I (61-Composite)
Gross Beta (Soluble-Grab) 12 12 1.01 4 8.8i.7 2.414.2 3.510.4 pCl/l pC1/1 (6A-Quarterly Gross Beta (Soluble-Composite) 12 12 1.21 4 3.01 5 1.811.5 Composite for Gross Beta (Insoluble-Grab) 12 10
<20 130190 45162 pCi/l Tritium)
Gross Beta 12 7
2713
<300 99+162 pCI/l (Insoluble-Composite) pCI/I Gross Alpha (Sotuble-Grab) 12 4
<.3 2.31.9
.8 11 Gross Alpha (Soluble-Composite) 12 2
<.3 311
.811.5 pCI/I Gross Alpha (Insoluble-Grab) 12 6
<9
<30 19110 pCi/l Gross Alpha (Insoluble-Composite) 12 5
1319
<80 35141 pCl/l
s TABLE IV (cont.)
SUMMARY
OF RADIDACTIVITY CONCENTRATIONS (N SAMPLES COLLECTED IN THE VICINITY OF PEACH BOTTOM ATOMIC POWER STATION, 1982 No. of Sample Type and Samples Number Period' Period' Period
Pre-op
l t_ oc at i on Analvsts Analvred Detected Mfnfmum Maximum Mean Mean Units 1
D1SCHARCE WATER PotentIalIy Aqueous Tritium (Grab) 12 3
<60 230170 901101 310!200 pCI/I Affected Aqueous Tritium (Composite) 12 3
<60 120170 77134 480130 pCI/I Stations Gross Beta (Soluble-Grab) 12 12 1.01 4 2.81 5 1.31.7 3.410.6 pCi/t (IM - Greb)
Gross Beta (Soluble-Composite) 12 12 1.11.5 2.61.5 1.91 7 3.410.6 pCl/l (IMM-Composite)
Gross Beta (insoluble-Grab) 12 10 3314 80170 45127 pCl/g Gross Beta (Insoluble-Composite) 12 11 40110
<100 64140 pCl/g Wett_ WATER On-Site Aqueous Tritium 8
1
<60 80170 70111 270!300 pCI/I Cells Gross Beta (Sol, e,le) 8 4
<.4
.91 4
.51 4 3.110.8 pCl/l (IU + IV)
Gross Beta (Inso.uble) 8 5
<60
<300 1201168 pCI/g Site Area Aqueous Tritium 4
2
<60 460180 1721168 4101100 pCI/I (40)
Gross Beta (Soluble) 4 3
<.4
.81.3
.51 4 3.010.1 pCf/l Gross Beta (Insoluble) 4 3
<80 3001200 197!238 pCI/g pCI/I Distant Aqueous Tritium 4
1
<60 410180 152 343 Dell (7)
Gross Beta (Soluble) 4 4
1.11 4 1.61 5 1.31 4 pCl/l Gross Beta (Insoluble) 4 pCi/g EdlN WATER On-Site (1A)
Gross Beta (Total) 12 12 311 1212 615 4.816.4 pCI/I Gross Beta (Total-Surf ace pCI/m2 Density) 12 12 170160 600i200 3261234 o
v v
m m
m r,
r-e-1 r,
r---
r-m TABLE IV (cont.)
SUPNARY OF RADIOACTIVITY CONCENTRATIONS IN SAWLES COLLECTED IN THE VICINITY OF PEACH BOTTOM ATOMIC POWER STATION, 1982 No. of Sample Type and Samples Number Period
- Period
- Period **
Pr e-op "
- J ocation Analvsis Analvred Detected Minimum Maximum Mean Mean Units i
RAIN WATER (cont.)
Distant (8)
Gross Beta (Total) 12 12 211 2012 819 pCi/l Gross Beta (Total-Surface Density) 12 12 1001100 11002200 4991674 pCi/m2 AIR PARTICULATES Weather Station Gross Beta 52 52
.0091 002
.0441 007
.0231 015 pCi/m3
- 1 (1Z) 52 51
< 004
.0361.006
.0211.013 pCI/m3 Distant (4A)
AIR lODfNE l-131 IB 52 0
<.005
<.053
<.017 pCI/m3 12 52 0
<.004
<.051
<.018 pCI/m3 2
52 0
<.011
<.051
<.018 pCl/m3 3r 52 0
<.011
<.051
<.019 pCI/m3 52 0
<.009
<.047
<.018 pCI/m3 6b 52 0
<.009
<.047
<.019 pCI/m3 14 52 0
<.009
<.082
<.029 pCi/m3 12D 52 0
<.003
<.041
<.014 pCI/m3 ILLW Near Farms Tritium (Aqueous Fraction) 8 6
<30 210150 811113 pCI/I (G,J,0)
(milk)
(G, J oniy for Tritium (Aqueous Fraction) 8 6
<70 280170 115 36 140f248 pCI/I Tritium)
(water) 1-131 114 0
<.03
<.26
<.07 0.2 pCI/I (milk)
Sr-89 (Quarterly-Grab, Farm J) 4 1
<1
<7 416 pCI/I (milk)
Sr-90 (Quarterly-Grab, Farm J) 4 4
2.51 7 11f6 617 pCI/I (milk)
Intermediate I-131 84 0
<.03
<.26
<.08 0.2 pCI/I Farms (D,L,M,N)
(milk)
TABLE IV (cont.)
SUf44ARY OF RADICACTIVITY CONCENTRATIONS IN SAMPLES COLLECTED IN THE VICINITY OF PEACH BOTTOM ATOMIC POWER STATION,1982 No. of Sample Type and Samples Number Period
- Period
- Period **
Pre-op*
Location Analvsts Analvred Detected Minimum Maximum Mean Mean Units
}i1111 (cont. )
Distant Farms Tritium (Aqueous Fraction) 8 5
<40 130160 73160 pCI/I (A,B,C,E)
(milk)
(A, C onIy for Tritium (Aqueous Fraction) 8 5
<70 150170 85157 103173 pCI/1 Tritium)
(water) 1-131 117 0
<.02
<.22
.02 pCI/I (milk)
SQ1L On-Si te Sr-89 (top 1")
2 0
< 01
<.08
<.05 pCi/g Location (dry)
(2)
(bottom) 2 0
<.06
<.08
<.07 pCI/g (dry)
Sr-90 (top 1")
2 2
.331.07
.50.06 421.24 2.1 pCi/g (dry)
(bottom) 2 2
.091 05
.161 05
.131 10 0.1 pCI/g (dry)
Distant Sr-89 (top 1")
4 0
<.05
<.07
<.06 pCl/g Location (dry) pCl/g (3A & 5)
(bottom) 4 0
<.05
<.09
<.07 (dry)
Sr-90 (top 1")
4 4
.081 04
.28.06
.151.20 0.6 pCI/g (dry)
(bottom) 4 3
<.03
.201 08
.121 15 0.4 pC1/g (dry)
All results above the MDL are quoted with a two sigma counting error.
A two sigma deviation of the data is' included with each mean. No value is given when only one result appears.
A two sigma devlution of the data is included with each mean. A dash Indicates that this analysis was not performed during the pre-operational period. Pre-op mean was calculated using pre-operational data where the minimum detectable levels were the same as those in 1974.
I L _ _1 O
Q
'O G
Q
~
TABLE V SUPO4ARY OF GAW4A SPECTROMETRY OF SAWLES COLLECTED IN THE VICINITY OF PEACH BOTTON ATOMIC POWER STATION, 1982
- OF
- PERl00*
PERIOD **
PRE-ope **
UNITS SA Wt_E TYPE ANALYZED FOUM)
DETECTED MINI ML34 MAXIMt94 MEAN MEAN Surface Water - Potentially Affected Stations (1Q, 4F, 4G,13A,13B - Grab) 57 K-40 1
1717 17 pCl/l (1LL, 4L - Composite) 24 None surface Water - Unaffected Stations (6A - Grab) 12 None pCI/I (61 - Composite) 12 K-40 1
140114 140 DIscharae Water - Potentially Affected Stations (1M - Grab) 12 None (IMM - Composite) 12 None Precinitatlon - On-site Station (I A - Composite) 12 Be-7 1
2319 23 pCI/l Preclottatlon - Distant Station pCI/I (8 - Composite) 12 Be-7 1
21 8 21 Air Particulates - Weather Station #1 3
(1Z) 12 Be-7 11 2817 13095 85169 10 3 pCI/m K-40 4
16d>
110116 45191 10 3 pCI/m3 Co-60 1
611 6
10 3 pCI/m3 Cs-137 1
.81.7
.8 10-3 pCl/m3 Alr Purriculates - Conowingo Dam (4A) 12 Be-7 11 39110 140114 81158 10 3 pCI/m3 3
K-40 1
38111 38 10 3 pCI/m H.LI.k - Near Farm (J) 4 K-40 4
12001120 16001160 14501383 pCI/I pCI/l Cs-137 2
til 211 211 Sci.L - On-site Location (2)
(Top 1")
2 K-40 2
6.71 7 1011 815 19i7 pCI/g(dry)
Sb-125 1
.21 2
.2 pCI/g(dry)
Cs-137 2
2.81.3 4.51.5 412 2tS pCI/g(dry)
Ra-226 2
.61 1
.91 1
.81 4 1.01.3 pCI/g(dry))
Th-232 2
.61 1
.91.2
.81 4 1.21 4 pCI/g(dry
TABLE V (cont.)
SumARY OF GAM SPECTROMETRY OF SAMPLES COLLECTED IN THE VICINITY OF PEACH BOTTOM ATOMIC POWER STATION, 1982
- OF
- OF SAMPLES SAMPLES
!!UCLIDES WITH NUCLIDE PERIOD
- PERIOD
- PERl00**
PRE-OP***
UNITS SAMPLE TYPE AMALYZED J OUND DETECTED MINIMUM MAXIMUM MEAN MEAN Sall - On-site Location (cont. )
(2)
(Bottom) 2 K-40 2
8.91 9 1411 1217 2315 pCI/g(dry)
Cs-137 2
491.05 2.01.2 112 114 pCI/g(dry)
Ra-226 2
.91 1 1.61 2 til 1.41.5 pCI/g(dry)
Th-232 2
.81 1 1.11 1 1.01 4 212 pCI/g(dry)
Sall - Distant Locations (3A & 5)
K-40 4
16f2 2713 20110 2114 pCl/g(dry)
Cs-137 4
.221 03 3.41.3 113
.61 8 pCI/g(dry)
Ra-226 4
.821 08 3.11.7 22
.81.9 pCI/g(dry)
Th-232 4
1.01 1 1.31 1 1.21.3 lit pCI/g(dry)
(Bottom) 4 K-40 4
1812 23f2 2014 21126 pCi/g(dry)
Cs-137 4
.211.03
.901 09
.51.8
.21.2 pCI/g(dry)
Ra-226 4
.811.08 2.41 7 112 lit pCI/g(dry)
Th-232 4
1.01 1 1.31 1 1.21.3
.911.1 pCI/g(dry)
All results above the POL are quoted with a two sigma counting error.
MDL values were not included. Period mean was calculated using only positive values for the nuclide listed.
Pre-op mean was calculated using only positive pre-operational values and not M)Ls for the nuclides IIsted. A dash indicates this analysis was not performed.
)
- c___,
u 4
ItMC TABLE VI StAttARY OF AISIENT DOSIDETRY PROGRAM STANDARD MONTHLY EQUIVALENT AVERAGE DOSE PERIOD PRE-OP( 1)
SAMPLE NO. OF sal #LES PERIOD PERIOD MEAN MEAN TYPE LOCATION ANALYZED MINIPRAt MAXIMLM i 2 SIGMA i 2 SIGMA lA81TS MONTHLY SITE 623 4.27 5 0.41 8.71 1 0.79 7.30 1 2.75 5.05 1 2.05 fetAD/STD. MONTH MIDDLE RING 1196 5.05 5 0.22 9.02 ; 0.30 7.49 1 2.32 5.7051.87 MRAD /STD. MONTH OUTER RING 332 5.65 ; 0.73 8.55 ; 0.57 7.11 1 2.22 5.8911.37 MRAD /STD. MohTH QUARTERLY SITE 207 3.42 3 0.36 8.98 ; 1.36 6.48 1 2.55 5.14 ; 1.60 tetAD/STD. Mt3fTH MIDDLE RING 600 3.75 1 0.28 8.85 ; 0.92 6.65 1 2.24 5.07 ; 1.25 MRAD /STD, MONTH OUTER RING 108 2.94 1 0.43 8.M i 0.61 6.42 1 2.76 5.44 5 1.70 MRAD /STD. MONTH THE PRE-OPTIONAL MEAN NAS CALCULATED FROM TLD READINGS 1-07-73 TO 8-05-76.
STATIONS IM, 31 AND 32 NERE ADDED TO THE PROGRAM 7-06-73 AND STATIONS 33A, 38, NERE NOT IN THE PRE-OPERATIONAL PROGRAM.
STATIONS liet AND 40 THROUGH 51 NERE ADDED TO THE PROGRAM ON 07-12-80.
SITE 80LMDARY RING STATIONS-18, IC,10, IE, IF,1G,1H, IJ, IL, IM, 1.94, 2, 40.
MIDDLE RING STATIONS
- 3A, 4K, 5, 68, 14, 15, 17, 22, 23, 26, 27, 31, 32, 33A, 38,
- 42, 43, 44, 45, 46, 47, 48, 49, 50, 51.
OUTER RING STATIONS
- 128, 16, 18, 19, 20, 218, 24.
NOTE: ALL SEMICOLONS INDICATE A PLUS OR MIteJS SIGN.
EXPOSURE PERIOD DATES ARE ItGICATED ON TABLES XXIII AND XXIV.
RNC TABLE VII ANALYTICAL' DATA FOR SURFACE NATER GRAB SANPLES CONCENTRATION IPC/Li STATION COLLECTION G. ALPHA G. ALPHA G. BETA G. BETA A.H3 CODE DATE SOLUBLE INSOLUBLE (A)
SOLUBLE INSOLUBLE EAD TOTAL le 82 01/09 1.6 i.4
< 20 100
- 80 02/06 1.6 i.5 34 55
< 60 03/06 1.7 i.4
< 20
< 70 04/03
.9 i.4 40 1 10
< 70 05/02 2.1 i.4 140 1 20
< 70 06/05 1.9 i.4 29
- 9
< 70 07/10 1.5 i.5 20 1 10 160
& 70 08/07 1.6 i.4 40 1 20 120
- 70 09/11 2.8 i.5
< 80
< 70 10/09 5.0
- .6
< 100
< 70 11/06 2.0 i.4 70 5 30 60 5 60 12/04 2.2 i.5
< 100
< 70 A M UAL HEANS..
2.1
- 2.1 58
- 79 83
- 60 4F 82 01/09
<.4 30 5 10 1.7 i.4 40 i 10 02/06
<.4 17 i7 1.8 i.5 36 i5 03/06
<.3
< 9 1.5 i.4
< 20
< 70 04/03
<.3 20 i 10 1.0 i.4 34 i8 05/02 1.5 i.7 30 1 10 1.5 i.4 35 67 06/05
<.7
< 9 1.9 i.4 70 5 20 07/10
.6 i.5 11
&8 1.9 i.5 29 i5
< 70 08/07
<.7 30 1 20 1.3
- .4 30 1 10 09/11
<.5
< 9 2.4 i.5 50 1 20 10/09
<.5 11 i8 2.0 i.5 60 1 30
< 70 11/06
<.8 11 1 10 2.5 i.5 33 56 12/04
<.6
< 10 2.2 i.5 140 5 30
< 70 APMJAL HEANS..
.6 i.6 16 i 18 1.8 i.9 48 i 64
< 70 4G 82 01/09 1.6 i.4 30 1 20 02/06 2.0 i.5 34 56 03/06 1.9 i.4
< 20 04/03 1.5 i
.4 30 i 10 05/02 1.8 i.4 240 5 40 06/05 2.0 i.4 40 i 10 07/10 1.5 i.5 20 i 10 08/07 1.8 i.4 30 1 30 09/11 2.5 i.5 60 5 20 10/09 1.7 i.5 60 1 40 11/06 2.3 i.4 70
- 60 12/04 2.2
- .5
< 60 A W UAL HEANS..
1.9 i.6 58 i 120 NOTE: ALL SEMICOLONS INDICATE A PLUS OR MINUS SIGN.
IA) REPORTED UNITS OF INSOLUBLE RESULTS ARE IN PC/ GRAM ASH.
.-_s w
w w
w -
r--
7--
1
-~
RMC TABLE VII (CONT.)
ANALYTICAL DATA FOR SURFACE WATER GRAB SAMPLES CONCENTRATION IPC/Li STATION COLLECTION G. ALPHA G. ALPHA G. BETA G. BETA A.H3 CODE DATE SOLUBLE INSOLUDLE (A)
SOLUBLE INSOLUBLE ( A)
TOTAL 6A 82 01/09
<.5 20 i 10 1.7 i
.4 30
- 20 02/06
.4 21 57 1.6
- .5 31 33 03/06
.5 i
.4 13
- 10 1.5
.4
< 20
< 70 04/03
<.3 16 i9 1.0
.4 40 i8 05/02 2.3 i
.9 20 i 10 1.7 i
.4 30 i 10 06/05
<.8 18 i9 2.0
.4 39 i 10 07/10
.5 i.5
< 9 1.6
.5 26
- 8
< 70 l
08/07 1
31
< 20 8.8
.7 40
- 20 09/11
<.8
< 30 3.0
.6 130
- 90 10/09
.9
< 20 1.4 i
.5 80 i 60
< 70 11/06
<.7
< 20 2.3 i.5 30
- 20 12/04
<.7
< 20 2.3 i.5
< 40
< 70 ANNUAL HEANS...
.8
- 1 19
- 10 2.4
- 4.2 45
- 62
< 70 13A 82 01/09 1.8 i
.4 50
- 20 C2/06 1.9
.5 33
- 5 03/06 1.6 i
.4 30
- 20 150 8 70 04/03 1.1
.4 37 i8 05/02 1.7
.4 80
- 30 06/05 1.9 i
.4 30 i 10 l
07/10 1.8 i.5 30 3 10
< 70 l
03/07 1.4 i
.4 30 3 20 C9/11 2.1
- .5 60 3 60 10/09 1.8
- .5
< 70
< 70 11/06 2.2
.4 90
- 40 12/04 2.4 i.s
< 70
< 70 ANNUAL HEANS...
1.8
- .7 51 3 45 90 8 80 138 82 01/25 2.0
- .5 50 3 20 03/15 1.8 i.5 25
- 9 04/14 1.4 i
.4 40 3 30 05/17 1.8
- .4 36 37 07/14 1.2 i.4
< 30 10/14 2.1
- .4 40 3 20 11/10 2.4
- .5 40
- 10 12/09 2.3 i
.4 24 54 ANNUAL MEANS...
1.9 i.8 35 i 18 NEAN (4F,13A)..
.6 i.6 16
- 18 1.8 i.8 49 i 54 80
- 57 MEAN (4F.6A 13A).
.7 i.9 18 3 14 2.0 1 2.5 48 3 56 77 3 46 MEAN
( 1Q,4 F.4G,13 A ).
.6 i.6 16
- 18 1.9
- 1.2 54 i 80 81
- 57 NOTE
- ALL SEMICOLONS ItOICATE A PLUS OR t1II US SIGN.
( Al REPORTED UNITS OF INSOLUCLE RESULTS ARE IN PC/GPAN ASH.
RMC TABLE VIII ANALYTICAL DATA FOR SURFACE HATER COMPOSITE SAMPLES CONCENTRATION (PC/L3 STATION COLLECTION G. ALPHA G. ALPHA G. BETA C. BETA I-131 A.H3 CODE PERIOD SOLUBLE INSOLUBLE (A)
SOLUBLE INSOLUBLE IA1 TOTAL TOTAL ILL 82 01/08-02/05 1.8 i.5 28 i8
< 60 02/05-03/05 1.5 i.4 32
- 8
< 70 03/05-04/02 1.1
.4 34
- 7
< 70 04/02-04/30 2.3
.4 39
- 7
< 70 04/30-06/04 1.5
- .4 40 1 10
< 70 06/04-07/09 1.6 i.5
< 10
< 70 07/09-08/06 1.4 i.4 20
- 10 100
- 70 08/06-09/10 2.8 i.5 40 1 30
< 70 09/10-10/08 1.8
- .5 50 1 30
< 70 10/08-11/05 2.2
- .4 30 1 20
< 60 11/05-12/03 2.2
- .5
< 100
< 70 12/03-01/07 1.8
- .3 90 1 50
< 90 At#UAL HEANS.........
1.8
- .9 43
- 53 73
- 23 4L 82 01/03-01/09
<.07 01/09-02/06
<.4
< 10 1.5
.4 30
- 20
< 60 01/30-02/06
.39 i.09 02/06-03/06
<.4 14
- 9 1.9
- .4 40 1 20 80 1 70 02/28-03/06
<.05 03/06-04/03
<.3 20
- 10 1.1 14 50 i 10
< 70 03/27-04/03
<.06 04/03-05/02 2.4 i.9 70 1 20 1.6
- .4 70 5 20
< 70 04/24-05/02
<.05 05/02-06/05
<.7 20 1 10 2.0 i.4 40 1 20
< 70 05/30-06/05
<.B4 06/05-07/10
<.4
< 10 1.3
- .5 20
- 20
< 70 07/03-07/10
<.08 07/10-08/07
<.8 20 i 10 1.2 i.4 29
- 9 100 i 70 07/31-08/07
<.09 08/07-09/11
<.5
< 10 2.1
- .5 40
- 30
< 70 09/04-09/11
<.04 09/11-10/09
<.6
< 20 1.5 i.5
< 60
< 70 10/02-10/09
<.06 10/09-11/06
<.7
< 20 2.6
- .5 30 1 20
< 60 10/30-11/06
<.07 11/06-12/04
<.8
< 30 2.4
- .5 70
- 70
< 70 11/27-12/04 iB) 12/04-01/08
<.5
< 50 2.0
)
.4
< 100
< 90 At#UAL MEANS.........
.7
- 1.1 24
- 36 1.8
- 1 48 i 46
.09
IA) REPORTED UNITS OF INSOLUBLE RESULTS ARE IN PC/ GRAM ASH.
(B) NO RESULTS COMPUTER HALFUFCTION.
l
\\
l s
m m
r--
1-f-
m l
RMC TABLE VIII (CONT.)
ANALYTICAL DATA FOR SUDFACE WATER COMPOSITE SAMPLES C0tlCENTRATION (FC/L)
STATION COLLECTION G. ALPHA G. ALPHA G. BETA G. BETA I-131 A.H3 CODE PERIOD SOLUBLE INSOLUBLE ( A)
SOLUGLE INSOLUBLE (A)
TOTAL TOTAL 6I 82 01/02-01/09
<.07 01/09-02/06
<.5 20 i 10 1.5 i.5 40
- 20
< 60 01/30-02/06
<.03 02/06-03/06
<.3 13 59 1.7 i
.4 30 5 20
< 70 02/27-03/06
.48 i.07 03/06-04/03
<.3 20 i 10 1.6 i.5 130 i 20
< 70 03/28-04/03
<.08 04/03-05/02 1.5 i.7 30
- 20 1.6 i.4 50
- 30
< 70 04/24-05/02
<.06 05/02-06/05
<.8
< 20 1.4 i.4 50 i 40
< 70 05/29-06/05
<.05 06/05-07/10
<.3 14
- 7 1.7 i. 5-27
- 3
< 70 07/03-07/10
<.09 07/10-08/07
<.8
< 30 1.2 i.4 120
- 40 100 1 70 07/31-08/07
<.09 03/07-09/11
<.6
< 40 2.3
- .5
< 100
< 70 09/04-09/11
<.09 09/11-10/09
<.6
< 80 1.8
- .5
< 300
< 70 10/02-10/09
<.07 10/09-11/06
<.7
< 50 3.0
- .5
< 70 70
- 60 10/31-11/06
<.07 11/06-12/04 3
- 1
< 60 2.4
- .5
< 200
< 70 11/27-12/04 (B) 12/04-01/08
<.6
< 40 1.6 i.3
< 70
< 90 ANNUAL MEAN..........
.8 8 1.5 35 8 41 1.8
- 1.0 99 8 162
.11
- .25 73 3 21 MEAN( 1LL,4 L ).........
.7
- 1.1 24 3 36 1.8 i
.9 45 5 49
.09 i.21 73 3 22 MEAN(ILL,4L,6I)......
.8
- 1.3 30 i 39 1.8 i
.9 63 i 111
.10 i.23 73
- 22 NOTE
- ALL SENICOLOftS INDICATE A PLUS CR HItUS SICN.
(A) REF07TED UNITS OF INSOLUDLE RESULTS ARE IN FC/GRAN ASN.
(B) NO RESULTS CCt!PUTER HALFUt.'CTION
TABLE IX CONCENTRATIONS OF GA MA EMlTTERS* IN SURFACE WATER IN THE VICINITY OF PEACH BOTTOM ATOMIC POWER STATION, 1982 Results in Units of pCI/I i 2 sigma GRAB SAMPLES Sample Dates Station Number 1-09-82 2-06-82 3-06-82 4-03-82 5-02-82 6-05-82 7-10-82 8-02-82 9-11-82 10-_09-82 11-06-82 12-04-82 IQ All<MDL AlI<MDL All<MDL All<MDL All<MDL All<MDL All<MDL Al l <EL All<WL All<MDL All<2L
' A l l <EL 4F All<MDL All<MDL All(MDL All<MDL All<MDL All(MDL All<MDL All<MDL All<MDL All<MDL All<MDL Al l <EL 4G All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL 6A All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL AII(MDL All<MDL Al l <@L Al I <@L 13A All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL Al!<MDL All<MDL All<MDL All<MDL All<MDL 13B(1)
All<MDL All<MDL All<MDL All<MDL All<MDL All< EL(2) Al l(WL All<MDL K-40 1717 l
Others (EL I
COMPOSITE SAWLES Sampling Period 1-09-82 2-06-82 3-06-82 4-03-82 5-02-82 6-05-82 7-10-82 8-07-82 9-11-82 10-09-82 11-06-82 12-04-82 Station to to to to to to to to to to to to rumber 2-06-82 3-06-82 4-03-82 5-02-82 6-05-82 7-10-82 8-07-82 9-11-82 10-09-82 11-06-82 12-04-82 1-08-83 ILLI3)
All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL All(MDL All(MDL All<MDL 4L All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL 61 All<MDL All<MDL K-40 140114 All<MDL All<MDL All<MDL All<MDL All<MDL All<MDL All(MDL All<MDL All<WL Others <@L a
For typical minimum detectable levels of nuclides searched for and not found, see Table XXVI.
(1)
Sampling dates for station 13B were 1/25/82; 3/15; 4/14; 5/17; 7/14; 10/14; 11/10; 12/09/82.
(2)
Specific date and time unknown.
(3)
Samp!Ing dates for station 1LL were 1/08/82-2/5; 2/5-3/5; 3/5-4/2; 4/2-4/30; 4/30-6/4; 6/4-7/9; 7/9-8/6; 8/6-9/10; 9/10-10/8; 10/8-11/5; 11/5-12/3; 12/3-1/07/83, a
- a w --
a
c,
__r-w
_i y_ _
1 r_
1 - - ~
r 1-
~_
.. m CHC TABLE X ANALTTICAL DATA FOR DISCHARGE WATER GRAB SAMPLES COHCENTRATION (PC/LI STATION COLLECTION G. BETA G. BETA A.H3 CODE DATE SOLU 3LE INSOLU3LE ( A)
TOTAL 1H 82 01/09 1.6 i.4 40 i 20
< 70 02/06 1.8 i.5 33 34
< 60 03/06 1.8 i.4 50
- 20 230 3 70 04/03 1.0 i.4 30 i 10
< 70 05/02 1.7 i
.4 50 i 10 90 i 70 06/05 1.5 i
.4 44 i9
< 70 07/10 1.9 i.5 39 i8
< 70 08/07 1.8 i.5 30 i 10 150
- 70 09/11 2.8 i.5
< 40
< 70 10/09 2.3 i.5
< 50
< 70 11/06 2.0 i
.4 50 1 20
< 60 12/04 1.9 i.4 80 i 70
< 70 ANNUAL MEAT!S...
1.8 i.9 45
- 27 90 i 101 RMC TABLE XI ANALYTICAL DATA FDR DISCHARGE HATER COMPOSITE SAMPLES
)
CotaCENTRATION (PC/L)
STATION COLLECTIDH G. BETA G. BETA A.H3 CODE PERIOD SOLUBLE INSOLUBLE ( A)
TOTAL IMH 82 01/19-02/05 2.1
- .5 40 i 10
< 60 02/05-03/05 2.0
- .4 60 i 10
< 70 03/05-04/02 1.9 i.5 80 3 20
< 70 04/02-04/30 1.7 i.4 80 i 10 90
- 70 04/30-06/04 1.9 i.4 70 i 10
< 70 06/04-07/09 1.6 i.5 40 i 10
< 70 07/09-08/06 1.7 i.4 40 3 10 120 i 70 08/06-09/10 1.1 i.5 40 1 20
< 70 09/10-10/08 2.2 i.5 80 3 50 90 i 70 10/08-11/05 2.2
- .4 70 8 40
< 60 11/05-12/03 2.6 i.5
< 100
< 70 12/03-01/07 2.0
- .4 70 i 60
< 90 ANNUAL MEAllS........
1.9 i.7 64 i 40 77 i 34 NOTE: ALL SEMICOLONS INDICATE A PLUS OR NINUS SIGN.
( Al REPORTED UNITS OF INSOLUBLE RESULTS ARE IN PC/ GRAM ASN.
2 2
3 8
L 8
8 L
3o7 40 0t0 l<
2 l
2 1
l 1
At 1
A 2
2 2
8 L
8 8
L D
6 6
M 5 o3 0
i 0t0 l
1 l
1 2
l 1
A 1
1 A
2 2
2 8
L 8
8 L
D 9
M 8o5 W
0 l
0t0 l
0 l
0 1
l A
1 1
A 1
2 L
2 2
L 8
E E
8 8
1 0o8 2
1 l
1 t0 8
l 9
9 Al 9
0 Al R1 1
ET,
AN WO I
2 L
2 2
L ET 8
8 8
m GA l
6o0 I
RT 7
V AS 0
l 0t1 I
X i
OR 8
A 8
9 AI X
SE e
I W
DO l
b P
2 L
2 2
a N
8 D
8 8
T l C M
S L
SO S
e l
E d
9o6 D
e 0
I s
1 L
o 0t0 M
e M
RT E
t 7
Al P
i 7
8 l
s r
l EA L
a A
e i
T P
D S
P Al d
X TM M
n E
I O A
g E
g u
L MT S
n n
2 2
L o
A O
B I
2 L
TI i
8 8
D f
B ET 8
D M
S M
T AB A
tp 5
O lp 4 o9 l
t MH G
a l
P m
0t0 R
m 0
AC S
6 Al O
S 6
7 Al o
M a
n GA C
d E
n FP a
O F r
~
SO 2
L 2
2 L
o N
8 D
8 8
D f
IOY M
M T
2 0 o4 AN l
d TI 0
l 3t0 l
he RI 5
Al 4
6 A
c TC r
NI a
EV e
C s
NE OH 2
L 2
2 L
s CT 8
D 8
8 D
e M
M id N
3 l
2 o0 l
l I
0 l
0t3 l
c 3
A 3
4 A
l 4
A 4
4 A
un fo 2
L 2
2 L
s 8
D 8
8 D
l M
M e
6 l
5 o2 l
e v
l 0t6 l
1 e
l ba w
t 2
L 2
2 L
c 8
D 8
8 D
e M
M t
0 l
5 o5 e
6 2
Al 0t0 l
d l
m 2
3 A
2 L
2 2
L i
J um in m
8 D
8 8
D l
M M
9o5 a
9 l
1 t0 l
c 0
l l
ip 1
A 1
2 A
y t
ro n
n F
or or
/
ie ie M
tb M
th M
am am 1
1 t
t u t u SN SN 1
il
,--y_
x
,-. r 1-c-
m r -,
1---,
c
'Et1C TABLE XIII ANALYTICAL DATA FOR WELL WATER SAMPLE 9 CollCENTRATION (FC/L)
STATION COLLECTION G.CETA G. BETA A.H3 CCDE DATE SOLU 3LE INSOLUBLE (A)
~~
10 82 01/09
.7 i
.4
.70 8 40
< 60 04/03
<.4 CD i 20
< 70 07/10
.5
- .4 100 3 20
< 70 10/09
< 4 190 i 70 80 " i 70 ANNUAL MEA!1S.....
.5 i.3 110 i 130 70 3 16 IV 82 01/09
.4 i.3
< 100
< 70 04/03
.9 i
.4 60 i 50
< 70 07/10
<.4
< 60
< 70 10/09
<.4
< 300-
< 70 AF#1UAL ME AttS.....
.5 i.5 130 3 230
< 70 7
82 01/10 1.3 i 4
< 200
< 70 04/05 1.1 i.4
< 60
< 60 07/11 1.6 i.5
< 70 410
- 80 10/10 1.2 i
.5 200 3 100
< 70 ANNUAL MEAftS.....
1.3 i.4 132 i 156 152 3 343 40 82 01/09
.8 i.3 300 3 200 100
- E0 04/03
.4 i.4 120 i 80
< 70 07/10
.5
.4
< CO 460
- 80 10/09
<.4 300 3 200
< 60 At#UAL ME ANS.....
.5 i.4 197 3 238 172 1 305 QUARTERLY !!Ef.ttS TRITIUM t A.H3). STATIONS IU AND IV
< 65 82 01/09
< 70 I
04/03
< 70 l
07/10 75 i 14 10/09 ALL set 11 COLONS It!DICATE A PLUS OR MIPUS SIGN.
NOTE:
(A) REFORTED UNITS OF INSOLUBLE RESULTS ARE IH PC/ GRAM ASH.
/
RMC TABLE XIV AtlALYTICAL DATA FOR PRECIPITATION SAMPLES CONC 9fTRATION (PC/L)
C0t1 CENTRATION (PC/SQ. M)
STATION COLLECTI0tt VOLUME STATION COLLECTION VOLUME CODE FERIOD (ML)
G. BETA C00E PERIOD (NL)
G. BETA lA 02 01/09-02/06 1500 7
- 2 1A 82 01/09-02/06 1500 300 i CD 02/06-03/06 1050 9
- 2 02/06-03/06 1050 310 i 50 03/06-04/03 1?00 4
32 03/06-04/03 1200 170
- 60 04/03-05/02 2550 3
51 04/03-05/02 2550 200 i 100 05/02-06/05 2933 4
- 2 05/02-06/05 2930 300 i 100 06/05-07/10 3000 5
- 2 06/05-07/10 3000 600 3 200 07/10-03/07 1000 12
- O 07/10-08/07 1000 360 i 60 08/07-09/11 1900 6
- 1 08/07-09/11 1900 340
- 80 09/11-10/09 2000 4
- 2 09/11-10/09 2000 200 i 100 10/09-11/06 2000 7
- 2 10/09-11/06 2000 430
- 200 11/06-12/04 2000 6
- 2 11/06-12/04 2000 400
- 100 12/04-01/03 2000 6
- 2 12/C4-01/08 2000 300
- 100 ANNUAL MEAtl........
6 i5 At#40AL ME Atl........ 326 3 234 8
82 01/09-02/06 1100 11
- 2 8
82 01/09-02/06 1100 360
- 60 02/06-03/06 900 10
- 2 02/06-03/06 900 280 3 40 03/06-04/03 1700 4
32 03/06-04/03 1700 230 3 90 04/03-05/02 2500 2
i1 04/03-05/02 2500 100 i 100 05/02-06/05 2055 5
32 05/02-06/05 2855 400
- 100 06/05-07/10 3800 9
- 2 06/05-07/10 3800 1100 ; 200 07/10-03/07 2000 9
32 07/10-03/07 2000 500
- 100 0S/07-09/11 1760 20 32 08/07-09/11 1760 1100 ; 100 09/11-10/09 2000 5
- 2 09/11-10/09 2000 300
- 100 10/09-11/06 3000 9
- 2 10/09-11/06 3030 800
- 200 11/06-12/04 2000 10 32 11/06-12/04 2000 600 i 100 12/04-01/0S 2000 4
- 1 12/04-01/03 2000 200
- 90 Af 81UA L llE Atl........
8
- 10 At#1UAL ME Atl........ 499 i 674 l
t!OTE: ALL SEMICOLCHS INDICATE A PLUS OR MINUS sigil.
n n
TABLE XV-CONCENTRATIONS OF GAM EMITTERS # IN PRECIPITATION IN THE VICINITY OF PEACH BOTTOM NUCLEAR POWER STATION, 1982 Results In Units of pCI/I i 2 sigma STATION 1A STATION 8 DATES NUCLfDES NUCLIDES 1-09-82 to 2-06-82 Be-7
<7 Be-7
<7 Others All<MDL Others -
Al l(@L
<14 Be-7
<14 2-06-82 to 3-06-82 Be-7
. All<MDL Others All<MDL Others 3-06-82 to 4-03-82 Be-7
<7 Be-7
<8 Others AII<MDL Others All(MDL 4-03-82 to 5-02-82 Be-7
<3 Be-7
<6 Others Al l <WL Others All<MDL 5-02-82 to 6-05-82 Be-7 2319 Be -7
<4 Others All<MDL Others All<MDL 6-05-82 to 7-10-82 Be-7
<4 Be-7
<4 Others AII<MDL Others All<MDL 7-10-82 to 8-07-82 Be-7 (4
Be-7
<10 Others All<MDL Others All<MDL 8-07-82 to 9-11-82 Be-7
<8 Be-7
<9 Others All<MDL Others All<MDL 9-11-82 to 10-09-82 Be-7
<7 Be-7
<8 Others All<MDL Others All<MDL 10-09-82 to 11-06-82 Be-7
<7 Be-7
<5 01hers All<MDL Others All<MDL 11-06-82 to 12-04-82 Be-7
<6 Be-7 21I6 Others All<mL Others Ali<2L 12-04-82 to 1-08-83 Be-7
<52 (1)
Be-7
<54 (II Others ALL<MDL Others ALL(MDL For typical minimum detectable levels of nuclides searched for and not found, see Table XXVI.
(1) High mL due to late counting as a result of computer malf unction.
$.. $. $. $... $.m m... $..
$..... g e
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TABLE XVil CONCENTRATIONS OF GAM 4A EMITTERS
- IN AIR PARTICULATES IN THE VIClhiTY OF PEACH BOTTOM ATOMIC POWER STATION, 1982 Results in Units of 10-3 pCI/m3 1 2 sigma Monthly Composite Periods Station 1-03-82 1-30-82 2-28-82 4-03-82 5-02-82 5-30-82 7-03-82 7-31-82 8-28-82 10-02-82 10-30-82 11-27-82 Mean Number to to to to to to to to to to to to i2 12 1-30-82 2-28-82 4-03-82 5-02-82 5-30-82 7-03-82 7-31-82 8-28-82 10-02-82 10-30-82 11-27-82 1-0-83 s.d.
Be-7 120121
<11 87111 130113 67112 89111 86110 100111 2817 130165 69113 3315 79 79 K-40
<13
<6
<11 12111
<14
<10 40+13
<11
<11
<20 110116 1615 23158 Co-60
<2
<.6
<1
<.7
<1
<.6 611
<.7
<.9
<1.6
<1
<4 213 Cs-137
<.9
<.6
<.8
.81.7
<.7
<.6
<.8
<.7
<.6
<1.3
<1
<.4
.81.5 Others
<MDL
<MDL
<MDL (MDL
<MDL
<MDL
<MDL
<MDL
<MDL
<@L
<MDL
<2L Monthly Composite Periods Station 1-03-82 1-30-82 2-28-82 4-03-82 5-02-82 5-30-82 7-03-82 7-31-82 8-28-82 10-02-82 10-30-82 11-27-82 Mean Number to to to to to to to to to to to to i2 4A 1-30-82 2-28-82 4-03-82 5-02-82 5-30-82 7-03-82 7-31-82 8-28-82 10-02-82 10-30-82 11-27-82 1-01-83 s.d.
Be-7 90112 (11 87+11 140+14 100+15 72+11 98111 79111 5118 39110 90114 4317 75169 K-40
<12
<8
<10
<11
<15 38+11
<13
<13
<8
<10
<18
<10 14116 Co-60
<.9
<.8
<.8
<.7
<2
<.7
<1
<1
<.5
<.7
<1
<.7
.91 8 Cs-137
<.6
<.7
<.6
<.7
<.9
<.7
<.9
<.7
<.5
<.6
<9
<.5
.71.3 Others
<MDL
<MDL
<MDL
<MDL
<MDL
<MDL
<MDL
<MDL (MDL
<MDL
<MDL
<MDL For detectable levels of nuclides searched for and not found, see Table XXVI.
7 TABLE XVill CONCENTRATIONS OF l-131 IN FILTERED AIR IN THE VICINSTY OF PEACH BOTTOM ATOMIC POWER STATION, 1982 Results in IJntts of 10-3 pCi/m3 + 2 Sigma STATION NUteER 1B 1Z 2
3A 5'
6B' 14' COLLECTION STATION NUM3ER CfM f Ff'T!"W DATE DATE 12D 1/03/82-1/09/82
<16.9
<15.3
<15.8
<15.3
<12.9
<13.6 (13.8 1/04/82-1/11/82
<13.3 1/09/82-1/16/82
<15.2
<15.1
<14.3
<14.4
<15.4
<15.6
<16.4 1/11/82-1/18/82
<11.9 1/16/82-1/24/82
<16.2
<15.7
<14.2
<15.3
<18.9
<18.4
<23.0 1/18/82-1/25/82
<13.1 1/24/82-1/30/82
<47.7
<33.0
<42.4
<42.3
<39.3
<39.9
<41.1 1/25/82-2/01/82
<17.1 1/30/82-2/06/82
<15.2
<14.4
<13.6
<14.1
<14.6
<14.5
<15.9 2/01/82-2/08/82
<17.2 2/06/82-2/13/82
<16.3
<15.5
<15.0 (14.i '
<15.6
<17.5
<15.6 2/08/82-2/16/82
<9.91 2/13/82-2/20/82
<24.0
<25.3
<20.2
<25.3
<19.4
<21.4
<20.2 2/16/82-2/22/82
<9.48 2/20/82-2/28/82
<21.6
<22.5
<23.9
<20.7
<35.8
<35.3
<36.8 2/22/82-3/01/82
<11.1 2/28/82-3/06/82
<17.1
<19.5
<1A.4
<19.1
<15.0
<15.6
<15.6 3/01/82-3/08/82
<12.4 3/06/82-3/14/82
<20.3
<18.1
<21.3
<f8.8
<19.0
<27.4
<27.5 3/08/82-3/15/82
<13.6 3/14/82-3/20/82
<18.1
<19.5
<20.2
<18.0
<67.2
<11.9
<12.4 3/15/82-3/22/82
<13.0 3/20/82-3/27/82
<13.1
<14.1
<15.0
<15.0
<12.6
<13.7
<12.9 3/22/82-3/29/82
<12.1 3/27/82-4/03/82
<14.2
<14.7
<13.8
. <15.2
<15.7
< 19.7
<18.1 3/29/82-4/05/82
<14.3 4/03/82-4/10/82
<19.7
<18.4
<21.5
<19.0
<21.7
<24.4
<22.2 4/05/82-4/12/82
<16.5 4/10/82-4/18/82
<12.2
<12.3
<13.5
<12.9
<11.8
<12.2
<11.7 4/12/82-4/19/82
<11.9 4/18/82-4/24/82
<14.8
<17.2
<24.8
<16.9
<20.0
<18.7
<11.8 4/19/82-4/26/82
<13.0 4/24/82-5/02/82
<10.4
<11.1
<11.8
<12.3
<10.9
<21.2
<10.8 4/26/82-5/03/82
<9.61 5/02/82-5/08/82
<13.0
<15.4
<15.5
<16.4
< 19.6
<21.1 (20.6 5/03/82-5/10/82
<11.6 5/08/82-5/16/82
<9.45
<10.9
<11.0
<11.1
<9.53
<10.0
< 9.70 5/10/82-5/17/82
<12.1 5/16/82-5/23/82
<12.1
<11.6
<13.2
<13.5
<16.6
<17.5
<16.2 5/17/82-5/24/82
<14.2 5/23/82-5/30/82
<12.1
<14.4
<14.5
<14.8
<14.9
<16.1
<14.6 5/24/82-6/01/82
<5.24 5/30/82-6/05/82
<15.1
<17.4
<17.9
<17.7
<14.4
<15.0
<14.6 6/01/82-6/07/82
<20.9 6/05/82-6/12/82
<14.6
<14.5
<16.7
<16.3
<15.0
<15.3
<14.9 6/07/82-6/14/82
<11.9 l
6/12/82-6/19/82
<15.9
<16.8
<17.2
<17.3
<15.7
<17.4
<17.0 6/14/82-6/21/82
<14.8 6/19/82-6/27/82
<9.46
<10.9
<11.8
<11.9
<13.8
<14.1
<14.5 6/21/82-6/28/82
<12.9 6/27/82-7/03/82
<32.8
<46.2
<40.0
<43.0
< 30.7
<33.0
<30.3 6/28/82-7/06/82
<27.8 7/03/82-7/10/82
<18.4
<18.2
<20.7
<19.0
<20.7
<20.1
<32.0 7/06/82-7/12/82
<40.6 7/10/82-7/18/82
<15.3
<17.0
<17.9
<19.5
<23.7
<24.5
<21.6 7/12/82-7/19/82
<20.9 7/18/82-7/24/82
<14.6
<16.8
<17.3
<18.6
<14.1
<14.2
<13.2 7/19/82-7/26/82
<7.33 7/24/82-7/31/82
<12.9
<14.9
<14.9
<16.5
<15.1
<15.0
<14.2 7/26/82-8/02/82 (20.9 7/31/82-8/07/82
<14.4
<16.3
<17.7
<18.2
<16.4
<20.4
<17.5 8/02/82-8/09/82
<17.1 8/07/82-8/15/82
<10.3
<12.0
<12.3
<13.8
<15.5
<17.9
<17.0 8/09/82-8/16/82
<13.0 8/15/82-8/21/82
<14.4
<16.9
<16.2
<18.0
<14.5
<15.7
<14.3 8/16/82-8/23/82
<11.7 8/21/82-8/28/82
<13.5
<15.5
<15.6
<17.5
<14.6
<16.0
<14.8 8/23/82-8/30/82
<3.36 8/28/82-9/04/82
<13.2
<16.8
<17.2
<18.2
<15.0
<15.7
<15.1 8/30/82-9/07/82
<11.2 9/04/82-9/11/82
<11.6
<13.3
<13.7
<15.9
<13.5
<14.2
<13.7 9/07/82-9/13/82
<14.9 9/11/82-9/18/82
<12.4
<15.4
<15.2
<16.9
<13.7
<15.2
<13.7 9/13/82-9/20/82
<15.4 9/18/82-9/25/82
<11.1
<11.2
<12.7
<11.9
<9.22
<9.10
<12.8 9/20/82-9/27/82
<17.0
.r---
w w.
TABLE XVill (cont.)
CONCENTRATIONS OF 1-131 IN FILTERED AIR IN THE VICINITY OF PEACH BOTTOM ATOMIC POWER STATION. 1982 Results in Units of 10-3 pC1/m3 + 2 Sigma STATION NUM3ER IB 1Z 2
3A 5'
6B' 14*
COLLECTION STATION NUE ER Col t FCTION DATE DATE 12D 9/25/82-10/02/82
<14.5
<14.8
<13.3 (29.7
<16.9
<14.0
<9.45 9/27/82-10/04/82' (19.5 10/02/82-10/09/82
<4.73
<14.6
<15.2
<15.6
<14.4
<15.7
<16.3 10/04/87-10/12/82
<5.51 10/09/82-10/16/82
<14.9
<14.8
<13.9
<15.1
<11.7
<11.2
<11.5 10/12/82-10/18/82
<14.8 10/16/82-10/23/82
<15.2
<15.2
<13.5
<15.6
< l 9.1
<18.6
<18.9 10/18/82-10/25/82
<5.94 10/23/82-10/30/82
<15.0
<15.3
<14.4
<15.5
<11.9
<11.7
<12.3 10/25/82-11/01/82
<12.1 10/30/82-11/06/82
<14.1
<14.0
<12.9
<14.9
<18.6 (16.4
<20.3 11/01/82-11/08/82
<12.9 11/06/82-11/13/82
<14.3
<13.3
<12.4
<14.5
<10.7
<11.0
<10.9 11/08/82-11/15/82
<11.3 t
i 11/13/82-11/20/82
<14.3
<13.6
<12.8
<14.5
<12.9
<11.9
<13.4 11/15/82-11/22/82
<11.4 11/20/82-11/27/82
<12.0
<27.3
<12.2
<12.1
<14.9
<14.5
<29.3 11/22/82-11/29/82
<10.8 11/27/82-12/04/82
<14.0
<22.2
<13.5
<14.9
<15.7
<14.5
<15.4 11/29/82-12/06/82
<11.4 12/04/82-12/11/82
<11.5
<4.15
<11.0
<11.6
<10.0
<9.13
<10.6 12/06/82-12/13/82
<10.9 12/11/82-12/18/82
<16.0
<15.6
<20.5
<20.2
<22.5
<25.0
<27.0 12/13/82-12/20/82
<18.3 12/18/82-12/24/82
<52.4
<50.6
<27.7
<46.5
<46.9
<46.5
<81.6 12/20/82-12/27/82
<10.5 12/24/82-1/01/83
<53.0
<50.7
<51.2
<51.4
<27.6
<45.2
<45.7 12/27/82-1/03/83
<33.1 1
Mean
<16.8
<17.9
<17.7
<17.7
<18.4
<18.5 (19.2
<14.1 Sampling dates for station 5, 68 and 14 in 1982 were as follows: 1/02-1/09; 1/09-1/16; 1/16-1/23; 1/23-1/30; 1/30-2/06; 2/06-2/13; 2/13-2/21; 2/21-2/27; 2/27-3/06; 3/06-3/13; 3/13-3/21; 3/21-3/28; 3/28-4/03; 4/03-4/10; 4/10-4/18; 4/18-4/24; 4/24-5/02; 5/02-5/07; 5/07-5/16; 5/16-5/22; 5/22-5/29; 5/29-6-05; 6/05-6/12; 6/12-6/19; 6/19-6/26; 6/26-7/03; 7/03-7/10; 7/10-7/17; 7/17-7/24; 7/24-7/31; 7/31-8/07; 8/07-8/14; 8/14-8/21; 8/21-8/28; 8/28-9/04; 9/04-9/11; 9/11-9/18; 9/18-9/26; 9/26-10/02; 10/02-10/09; 10/09-10/17; 10/17-10/23; 10/23-10/31; 10/31-11/06 11/06-11/14; 11/14-11/21; 11/21-11/27; 11/27-12/04; 12/04-12/12; 12/12-12/18; 12/18-12/24; 12/24-1/01/83.
s
Table XIX -
Concentrations of I-131 and Tritium in Milk in the Vicinity of Peach Bottom Atomic Power Station,1982 Results In Units of pCi/l i 2 sigma 1-131 ColIectIon Date Station A Station B Station C Station D Station E Station G Station J Station L Station M Station N Station 0 1/18/82
<.04
<.04
<.04
<.05
<.05
<.05
<.05
<.04
<.04
<.04
<.06 2/15/82
<.05
<.04
<.05
<.06
<.06
<.06
<.05 3/22/82
<.05
<.05
<.05
<.06
<.06
<.06
<.06
<.06 3/29/82
<.04
<.05
<.05
<.06
<.06
<.06
<.11
<.06 4/05/82
<.07
<.11
<.11
<.07
< 08
.<.09
<.10
<.08 4/12/82
<.05
<.06
<.07
<.07
<.07
<.08
<.06
<.07 4/26/82
<.05
<.05
<.06
<.06
<.05
<.06
<.06
<.05 5/03/82
<.04
<.04
<.04
<.05
<.05
<.06 (1)
<.05
<.04
<.05
<.05 (1)
<.06 (1) 5/10/82
<.05
<.06
<.06
<.05
<.06
<.05
<.06
<.06 5/17/82
<.05
<.05
<.05
<.06
<.05
<.06
<.07
<.05 5/24/82
<.05
<.04
<.05
<.05
<.05
<.06
<.05
<.06 5/31/82
<.05
<.05
<.05
<.06
<.06
<.06
<.06
<.06 6/07/82
<.02
<.02
<.03
<.03
<.03
<.03
<.03
<.03 6/14/82
<.05
<.05
< 06
<.06
<.07
<.07
<.06 6/21/82
<.04
<.04
<.05
<.05
<.05
<.06
<.06
<.05 6/28/82 (2)
<.05
<.07
<.07
<.09
<.09
<.09
<.12 7/ 06/ 82
<.14
<.13
<.18
<.21
<.14
<.18
<.17
<.14 7/12/82
<.16
<.07
<.12
<.12
<.17
<.15
<.15
<.17
<.08
<.16
<.15 7/19/82
<.05
<.05
<.09
<.10
<.10
<.12
<.11'
<.10 7/26/82
<.03
<.04
<.05
<.05
<.05
<.08
<.10
<.07 8/02/82
<.05
<.07
<.08
<.06
<.07
<.08
<.10
<.07 8/09/82
<.06
<.08
<.09
<.08
<.09
<.06
<.09
<.09 8/16 82
<.06
(.06
<.05
<.05
<.05
<.06
<.06
<.05 8/23/82
<.04
<.04
<.04
<.05
<.06
<.06
<.04
<.06 8/30/82
<.05
<.06
<.03
<.04
<.05
<.05
< 07
<.04 9/06/82
<.08
<.05
<.04
<.07
<.07
<.08
<.11
<.08 9/13/82
<.05
<.06
<.04
<.04
<.05
<.05
<.05
<.05 9/20/82
<.04
<.04
<.05
<.04
<.04
<.04
<.05
<.05 9/27/82
<.06
<.08
<.07
<.07
<.08
<.08
<.09
<.07 10/04/82
<.04
<.05
<.05
<.05
<.05
<.08
<.06
<.06 10/11/82
<.07
<.06
<.06
<.05
<.07
<.07
<.07
<.06 10/18/82
<.06
<.05
<.05
<.06
<.05
<.06
<.07
<.06 10/25/82
<.06
<.07
<.06
<.06
<.07
<.08
<.08
<.07 11/01/82
<.06
<.07
<.07
<.07
<.06
<.07
< 07
<.08
<.09
<.07
<.07 11/08/82
<.06
<.06
<.06
<.07
<.07
<.06
<.07
<.08 11/15/82
<.05
<.05
<.05
<.07
<.06
<.06
<.06
<.05 11/22/82
<.08
<.08
<.05
<.07
<.05
<.07
<.06
<.06 12/13/82
<.16
<.13
<.13
<.26
<.21
<.18
<.21
<.26 Mean
<.06
<.06
<.07
<.08
<.07
<.07
<.08
<.07
<.08
<.07 s
w
w J
Table XIX (cont)
Concentrations of I-131 and Tritium in Milk in the Vicinity of Peach Bottom Atomic Power Station,1982 l
Results in Units of pCi/l i 2 sigma Tritium ColIection A
C G
J Dates Milk Water Milk Water Milk Water Milk Water 1/18/82
<60
<70 130i60 150i70 210150 280170
<60
<70 5/03/82
<70
<70
<70
<70 80170 90170 89160 110170 7/12/82
<40
<70
<40
<70 84150 100170
<30
<70 l
11/01/82 72160 80170 99170 100170 35120 100170 60140 100170 i
Mean 61129 38187 85177 98126 1021150 1431184 60148 88141 (1) Collection date was 5/02/82.
(2)
Sample lost in shipping.
TABLE XX WEEKLY MEAN CONCENTRATION OF l-131 IN MILK IN THE VICINITY OF PEACH BOTTOM ATOMIC POWER STATl0N,1982 i
Results in Units of pCI/I i 2 sigma Collection Near Farms Intermediate Farms Distant Farms-Date (G.J.0)
(D.L.M.N)
(A.B.C.E)
All Farms 01/18/82
<.052
<.043
<.043
<.045 I
02/15/82
<.056
<.057
<.047
-<.053 03/22/82
<.059
<.059
< 048
<.055 03/29/82
<.061
<.083
<.045
<.061 04/05/82
<.085
<.088
<.097
<.090 04/1.2/ 82
<.071
<.065
<.058
<.065 04/26/82
<.055
<.059
<.056
<.056 05/02/82-05/03/82
<.0 56
<.048
<.044
<.335 05/10/82
<.056
<.055
<.056
<.056 05/17/82
<.052
<.062
<.050
<.054 05/24/82
<.054
<.052
<.048
<.051 05/31/82
<.063
<.060
<.047
<.057 06/07/ 82
<.029
<.029
<.023
<.026 06/14/82
<.066
<.065
<.051
<.061 06/21/82
<.054
<.056
<.044
<.051 06/28/82
<.101
<.085
<.063
<.085 07/ 06/82
<.153
<.192
<.151
<.162 07/12/82
<.149
<.132
<.128
<.135 07/19/82
<.105
<.101
<.065
<.089 07/to/82
<.06 8
<.075
<.041
<.060 08/02/82
<.073
<.061
<.067
<.069 08/09/82
<.080
<.087
< 075
<.080 08/16/82
<.053
<.057
<.055
<.055 08/23/ 82
<.061
<.047
<.043
<.051 08/30/82
- <.047
<.053
<.047
<.089 09/06/82
<.074
<.087
< 056
< 070 09/13/82
< 048
<.050
<.051
<.049 09/20/82
<.045
<.041
<.041
<.043 09/27/82
<.077
<.076
<.070
<.074 10/04/82
<.062
<.056
<.045
<.054 10/11/82
<.066
<.063
<.063
<.06 4 10/18/82
<.057
<.065
<.052
<.057 10/25/82
<.073
<.073
<. 06 4
<.069 11/01/82
<.068
<.077
<.064
<.070 11/08/82
<.071
<.073
<.061
< 068 11/15/82
<.058
<.065
<.048
<.056 11/22/82
<. 06 0
<.066
<.075
<.067 12/13/82
<.217
<.235
<.140
<.193 m
TABLE XXI CONCENTRATIONS OF Sr-89, Sr-90 AND GAMMA EMITTERS
- lN MILK IN THE VICINITY OF PEACH BOTTOM ATOMIC POWER STATION, 1982 Results in Units of pCI/I i 2 sigma STATION SAMPLING NUCLIDES FOUND NUMBER DATE Sr-89 Sr-90 K-40 Cs-137 J
1-18-82
<7 11 6 16001160 211 5-03-82
<2 511 16001160
<.6 7-12-82 613 512 1400i140
<.5 l
l 11-01-82
<1 2.5.7 12001120 til Mean 2 s.d.
416 617 14501383 til For typical min! mum detectable levels of nuclides searched for and not found, see Table XXVI.
m TABLE XXll CONCENTRATIONS OF Sr-89, Sr-90 and GAM EMITTERS
- IN SOIL IN THE VICINITY OF PEACH BOTTOM ATOMIC POWER STATION, 1982 Results in Units of pCl/g(dry)
~
Env. Station No.
STATION 2 Average STATION 3A STATION 5 Average of Site Distant Date 4-18-82 10-30-82 Location 4-18-82 10-30-82 4-18-82 10-31-82 Locations Sr-89 top 1"
<.08
<.01
<.05
<.07
<.07
<.05
<.06
<.06 bottom
<.06
<.08
<.07
<.09
<.05
<.06
<.07
<.07 Sr-90 top 1"
.501.06
.331.07
.421 24
.281.06
.171.04
.081.04
.071 04
.151.20 bottom
.161.05
.091 05
.131 10
.201.08
<.03
.081 06
.151.05
.121.15 K-40 top 1" 6.71.7 1011 8.414.7 1612 17 2 27f) 1912 19.8110.0 bottom 8.91.9 1411 11.517.2 1812 1912 23f2 1912 19.814.4 Sb-125 top 1"
.21 2
<.1
.21 1
<.07
<.09
<.06
<.05
<.07 bottom
<.09
<.'0 8
<.09
<.06
<.08
<.05
<.05
<.06 Cs-137 top 1" 4.51.5 2.81 3 3.712.4
.921.09 3.41.3
.641.06
.221 03 1.3 2.9 bottom 2.01.2
.49i.05 1.212.1
.901.09
<.03
.211 03
.231.03
.341 76 Ra-226 top 1"
.61.1
.91 1
.8.4 1.11 1 3.11 7 1.01.1
.821.08 1.512.1 bottom
.91.1 1.61 2 1.311.0 1.11 1 2.41.7
.841.08
.811 08 1.311.5 Th-232 top 1"
.61.1
.91.2
.81 4 1.11 1 1.21 1 1.31 1 1.01 1 1.21.3 bottom
.81.1 1.11.1 1.01.4 1.2.1 1.11 1 1.3i.1 1.01 1 1.21 3 Others top 1"
<MDL
<MDL
<MDL
<MDL
<MDL
<MDL
<MDL
<MDL l
bottom
<MDL
<MDL
<MDL
<MDL 41DL
<MDL
<MDL
<MDL l
For typical minimum detectable levels of nuclides searched for and not found, see Table XXVI.
.~
1 o
m
f.m rx m _
m e
r RfC TABLE XXill IWNTHLY TLD RESULTS RESULTS IN LMITS OF fotAOS/STO. MONTM
' STATION 82 82 82 82 82 82 82 82 82 82 82 83 CODE E9V.MO. AVG. 01/09-02/06 02/06-03/06 03/06-M/03 04/03-05/02 05/02-06/05 06/05-07/10 07/10-08/07 08/07-09/1109/11-10/0910/09-11/M 11/M-12/04 12/04-01/15 1A 7.90 i 1.51 7.0510. M 9.0250.79 6.9310.64 7.7050.75 7.1150.86 7.2350.77 8.0750.78 7.6652.05 8.9550.68 8.4060.37 8.77;1.59 8.1550.49 13 6.3711.34 5.6910.57 7.4151.26 5.9810.41 7.1511.21 6.5710.70 5.77&O.25 6.4350.57 5.2411.14 6.9550.68 6.8950.41 6.4850.96 6.0050.60 1C 7.75 i 0.99 6.9150.33 8.3750.46 7.5850.36 8.5150.90 7.9911.94 7.6810.72 8.0750.35 7.2151.53 7.7251.30 8.3210.90 7.6350.44 7.31;1.07 10 7.39 5 1.35 6.7651.01 7.6210.82 6.6950.30 8.1051.00 7.5350.91 7.4050.22 7.0450.57 6.2550.89 7.63;1.05 7.9750.83 8.7150.72 7.2350.79 IE 7.38 ; 1.71 7.1250.62 7.76;0.92 6.410.74 8.7451.49 7.5250.98 7.3350.62 7.3350.24 6.7010.41 7.4411.41 8.0450.72 7.5350.77 6.9460.94 1F 8.67 8 1.59 8.2750.81 9.9251.44 7.95;1.29 9.5750.81 8.68;2.12 7.7550.86 9.4310.65 7.8851.59 7.8450.89 9.0510.90 9.70;1.54 8.5450.72 13 5.80 i 1.47 5.3150.30 6.5810.84 5.55&c.71 6.3810.37 5.1150.53 5.9410.68 5.3410.39 4.6350.97 7.1651.87 5.9750.32 6.6110.40 5.5050.26 1H 7.53 ; 0.95 6.7650.52 8.0410.28 6.940.39 8.3110.88 7.1750.77 7.7050.86 7.1960.55 7.3350.40 7.8250.72 8.0711.23 7.4611.52 7.5810.77 II 6.00 i 1.22
- 5. Mil.01 7.0350.32 5.8450.79 6.9650.28 5.7810.85 5.8960.72 5.6250.59 4.8250.88 6.5950.50 6.0650.32 - 6.2011.07 5.9650.93 IJ 8.71 ; 0.96 8.1251.04 8.7450.72 8.7351.62 8.7850.78 8.99;1.20 8.43;1.46 8.5550.51 8.0351.80 8.5110.77 9.4750.74 9.6951.31 8.7110.79 IL 6.46 ; 1.38 5.9350.84 7.0110.09 6.2050.41 6.0450.56 5.6850.52 5.8150.34 6.6050.60 5.6310.30 7.3250.83 7.4310.72 7.3850.93 6.8550.85 1M 4.33 i 1.30 4.2750.41 5.2450.55 4.4450.95 4.6250.39 4.10 io.M 4.1950.24 4.3250.29 3.0650.53 4.0750.35 5.2010.28 5.3050.32 3.7950.23 2
7.32 i 1.36 6.5450.27 7.6450.98 6.7180.70 8.04;0.87 7.1910.24 7.08;0.52 6.7910.27 6.6950.68 8.2210.32 8.3950.47 8.0950.M 6.8650.49 3A 5.70 1 0.92 5.Mio.62 6.2650.44 5.6250.40 5.8750.16 5.6280.58 6.0750.22 5.1710.36 4.7611.04 6.3750.44 5.6550.63 6.1580.43 5.4850.51 4K 4.90 1 0.75 5.0560.22 5.5750.76 4.6950.50 5.2350.69 4.6310.49 5.09 0.48 4.5450.26 4.4250.51 4.9150.60 5.4650.45 4.9750.89 4.5150.41 5
6.96 ; 1.23 6.2750.38 7.2810.47 6.10;1.02 7.1250.48 6.7250.99 7.3310.44 7.3150.69 6.4050.83 6.8051.20 7.9050.76 8.0250.78 6.6050.59 68 6.07 i 1.30
- 5. %;0.30 7.1750.90 6.6251.76 6.8250.41 6.1710.64 5.M10.54 5.8851.06 4.e7;1.30 6.2450.57 6.4250.48 6.2510.%
5.5750.31 14 7.33 ; 1.19 7.1260.88 7.7950.81 7.5350.35 7.7750.55 8.06 50.M 7.54;1.25 7.4550.46 5.6550.64 7.1481.13 7.4350.60 7.4150.41 7.3350.91 15 7.43 i 1.67 6.6850.48 7.7650.68 6.7750.30 8.0651.05 7.0250.68 6.8650.25 7.4350.53 5.9650.75 8.3310.80 8.6150.52 8.58;1.07 7.6360.34 16 7.45 i 1.40 6.2450.76 8.3050.44 6.89 50.M 8.0110.73 7.7410.31 7.3851.30 7.2750.75 6.1850.88 7.62;1.52 7.8751.80 8.2010.80 7.7650.58 17 8.33 1 1.04 7.8250.51 8.9250.93 8.1350.87 8.1850.'35 8.4751.18 7.8110.65 7.7851.03 7.5451.25 8.7050.60 8.7050.29 8.9151.16 9.0250.30 l
18 7.62 ; 1.97 7.0250.87 8.5010.40 7.1950.37 7.9650.52 7.9050.63 6.8150.57 6.5250.61 5.8650.69 8.7911.23 9.2010.67 8.1560.96 7.9250.41 19 7.35 i 1.45 6.7950.91 7.7710.75 6.4610. %
8.0650.91 7.5010.71 6.7050.94 6.8610.22 6.8611.61 7.7611.08 8.97;1.01 7.8560.91 7.0580.36 20 8.34 5 1.06 8.1610.60 9.4150.37 8.2650.51 8.8150.56 8.1911.04 8.1450.96 7.7150.28 7.3851.00 8.79;1.19 8.6050.54 8.2411.22 8.5550.57 213 7.08 ; 1.71 6.1010.35 7.87;1.48 6.8710.38 7.46;0.42 7.3251.08 6.8410.33 6.3950.32 6.0310.89 6.5151.01 8.9250.82 7.9750.58 6.9450.78 NOTE: ALL SEMICOLONS IfSICATE A PLUS OR MIP8IS SIGN.
RHC TABLE XXill (CONT. )
HONTHLY TLD RESULTS RESULTS IN LNITS OF HRADS/STO. HONTH STATION 82 82 82 82 82 82 82 82 82 82 82 83 CODE EQV.HO. AVG. 01/09-02/06 02/06-03/06 03/06-C4/03 04/03-05/02 05/02-06/05 06/05-07/10 07/10-08/07 08/07-09/1109/11-10/0910/09-11/06 11/06-12/D412/C6-01/15 22 7.14 5 1.11 6.9911.12 7.8950.29 6.8511.12 6.8510.47 7.2950.42 7.5510.50 6.1550.87 6.1450.91 7.3350.20 8 1451.20 7.0610.31 7.4150.49 23 7.56 5 1.21 7.1250.88 8.3651.28 7.3551.03 7.6710.19 7.5750.98 8.0350.71 7.0150.47 6.2250.41 7.6250.71 8.2410.84 8.1881.21 7.5650.51 24 5.90 i 1.33 5.6550.73 6.8750.80 5.4261.42 6.3150.65 5.7450.46 6.0610.66 4.97;0.29 4.8560.81 6.2650.54 6.9650.74 6.2650.67 5.7350.46 2$
8.08 ; 1.43 7.47;1.49 8.8751.00 7.7310.46 8.7351.47 7.67&1.30 7.9550.26 7.9211.11 6.6450.78 8.3350.48 9.0150.75 9.0060.75 8.0850.25 27 7.84 ; 1.57 6.8350.76 8.9250.76 7.5750.62 8.20;1.07 7.7050.84 8.3250.92 7.14;0.26 6.5411.06 7.8360.34 9.1050.68 8.4250.60 7.7950.60 l
l 31 7.55 i 1.23 6.9030.50 7.9050.77 7.6310.37 7.8610.20 7.2010.48 7.7810.72 6.8451.44 6.8350.79 7.5850.72 8.8810.55 8.2350.92 7.2950.64 32 8.01 1 1.46 7.4150.32 8.4610.75 8.2450.78 8.3150.50 7.4750.75 8.4350.58 7.1750.30 6.7351.51 8.3610.30 9.1310.61 8.9851.14 7.8550.69 33A 5.94 ; 2.29 5.3110.82 6.9410.62 5.5850.90 5.9660.67 5.9450.48 6.6450.26 4.31&O.32 4.2650.19 8.3410.16 6.1950.29 6.88&c.76 5.4550.74 l
33 7.96 6 1.29 7.64;1.26 8.2250.79 8.3350.13 8.5551.22 7.3810.38 8.5010.21 7.3410.21 6.8051.34 7.9610.96 9.1360.74 8.3360.46 7.7181.19 40 8.44 5 1.39 7.8350.97 9.2550.52 8.4451.52 8.3950.53 9.02;1.01 8.3550.88 8.3110.51 6.9350.47 8.5851.25 9.1351.14 9.4650.67 8.0851.06 42 8.71 i 1.73 8.8950.94 10.1210.37 8.4050.56 9.0410.75 9.4750,69 8.8061.04 7.24;0.36 6.9750.49 8.8750.81 8.7110.42 9.1551.40 8.9310.45 43 8.81 1 1.35 7.8250.62 9.4350.77 7.8610.41 9.1551.71 9.0851.92 9.7810.61 8.2010.66 8.65;1.09 9.42;1.85 9.5110.11 8.4450.97 8.3551.05 44 6.96 i 1.08 6.7450.52 7.7310.46 6.8650.42 7.0850.64 6.3950.50 7.3750.53 6.2310.85 6.5350.60 7.6650.54 7.8050.83 6.7010.87 6.7050.30 45 7.86 5 1.48 7.3610.80 9.0250.48 7.1050.52 8.6150.59 7.6060.89 8.2850.62 6.4110.27 7.4051.64 8.6450.58 8.1750.36 8.05;0.39 7.8051.36 46 6.90 i O.97 6.4450.76 7.2810.85 6.2550.58 7.7050.42 6.5650.26 7.1450.43 6.4550.40 6.78;0.11 7.6311.09 IAI 6.86&1.31 6.8661.02 47 8.56 5 0.97 8.0650.29 9.1450.33 8.3850.61 8.8911.03 8.2410.59 8.4250.70 7.49;1.02 8.8760.58 8.7110.53 9.2251.15 8.54;1.04 8.7350.37 48 7.68 i 1.28 7.7951.36 8.6850.64 6.65;1.06 8.0250.24 8.0611.43 8.1910.45 6.4910.93 7.2251.22 7.7050.91 8.1450.89 7.85;1.11 7.4130.49 49 8.19 i 0.97 7.7211.03 8.3850.82 7.9250.70 8.6360.42 8.4710.93 7.8550.87 7.7750.90 7.80;0.99 7.98i1.61 9.3310.99 8.6151.36 7.9850.57 50 8.59 5 1.85 7.1510.36 9.2311.28 8.4250.47 9.5951.80 8.9611.16 8.8651.24 8.3350.37 6.5350.40 8.8250.30 9.6850.90 8.9550.87 8.7550.66 S1 7.75 i 1.39 7.3850.63 8.4210.58 7.5850.32 8.3560.58 8.1281.39 8.3950.81 7.0251.02 6.3860.59 6.9850.49 8.6110.76 8.0510.85 7.7650.46 INN 8.40 i 1.80 8.0150.56 9.0350.64 8.6150.89 8.8050.24 8.6950.57 9.36;1.29 7.1250.20 6.5950.26 8.2551.35 8.9750.51 9.74;1.31 8.0250.76 82 82 82 82 82 82 82 82 82 82 82 83 STATICt4 01/06-02/08 02/04-03/05 03/05-04/06 03/31-04/28 04/27-06/08 06/02-07/08 07/08-08/10 08/01-09/14 09/07-10/0810/C8-11/0311/02-12/01 12/01-01/18 CODE EQV.HO. AVG.
12B 5.77 5 1.06 5.7150.68 6.3050.43 6.2319.82 6.1550.74 5.8050.50 5.5250.39 5.1250.35 4.8150.57 5.8010.53 5.65;0.52 6.7810.58 5.9250.64 NOTESt ALL SEHICOLONS INDICATE A PLUS OR HINUS SIGN.
t i
ta w
w w
+
.~
- w__,
.~-,
RMC TABLE XXIV GUARTERLY TLD RESULTS RESULTS IN UNITS OF MRAOS/STD. MONTH STATION 82 82 82 83 STATION 82 82 82 83 CODE E9V.MO. AVG. 01/09-04/03 04/03-07/10 07/10-10/09 10/09-01/15 CODE E9V.MO. AVG. 01/09-04/03 04/03-07/10 07/10-10/09 10/09-01/15 1A 7.20 1 2.02 6.1980.76 6.56t0.28 7.4610.28 8.45;1.65 22 6.30 1 0.90 5.7910.59 6.6050.18 6.0950.23 6.6910.32 18 5.71 1 0.87 5.0910.63 5.7850.32 5.7510.27 6.13;0.31 23 7.06 ; 1.86 6.0710.77 7.0350.22 6.6910.04 8.2850.52 l
IC 6.72 i 1.26 5.83;0.30 6.6950.34 6.9810.27 7.2910.44 24 5.49 ; 1.26 4.55;0.39 5.6250.24 6.0050.35-5.7150.63 j
1 f
ID 6.63 i 1.71 5.4550.53 6.5150.15 7.4550.31 6.9981.07 26 7.70 i 1.53 6.5310.22 7.8550.26 8.1250.18 8.1510.44 l
1E 6.72 i 0.78 6.2150.35 6.5650.38 7.0510.35 7.0010.40 27 6.84 5 1.84 5.8051.11 6.2850.43 7.4510.20 7.7250.70 IF 7.82 i 1.46 6.7950.45 7.7150.33 8.3010.36 8.3711.07 31 6.73 1 1.17 5.9910.67 6.5550.34 7.3810.18 6.9330.83 IG 5.16 5 0.98 4.48;0.96 5.3050.14 5.1250.16 5.6510.98 32 7.06 i 1.29 6.1810.22 6.9850.28 7.6910.15 7.3250.96 1H 6.42 1 0.78 5.9450.32 6.8950.17 6.3210.10 6.4650.29 33A 5.03 3 0.70 4.4850.14 5.1850.38 5.17;0.21 5.2150.67 II 5.41 1 1.01 4.6810.64 5.7050.28 5.3650.31 5.8050.34 38 7.06 i 1.18 6.17;0.45 7.17;0.32 7.4610.06 7.33;0.92 IJ 7.92 5 2.35 6.6750.91 7.1010.16 8.8010.19 8.98i1.36 40 7.63 ; 0.75 7.1751.38 7.6751.02 8.0950.22 7.57;1.45 IL 5.65 1 0.93 5.2110.57 5.2750.14 5.9110.27 6.1550.66 42 8.15 i 1.62 6.9650.87 8.2110.80 8.4110.24 8.8550.92 1M 3.83 5 0.64 3.4210.36 4.1050.23 3.7050.23 4.0510.37 43 7.63 i 1.67 6.8050.44 7.0610.44 8.60;0.48 8.0150.51 2
6.46 5 1.02 5.74;0.50 6.4150.25 6.6710.14 6.9350.54 44 6.16 ; 0.31 6.0050.31 6.1850.64 6.0610.20 6.3610.25 3A 5.03 1 0.86 4.3980.70 5.0910.29 5.3050.14 5.2810.81 45 7.10 1 1.08 6.4050.37 7.0350.63 7.7150.18 7.2110.65 4K 4.22 1 0.70 3.7550.28 4.1150.13 4.5650.29 4.40;0.48 46 6.24 i 1.79 5.0250.69 6.2350.49 6.3450.32 7.1911.00 5
6.00 1 1.09 5.4910.26 5.9050.14 5.7750.38 6.7610.32 47 7.79 ; 1.21 6.9710.32 7.7910.84 8.4410.07 7.8950.48 68 5.35 5 0.88 4.7450.33 5.6850.26 5.65;0.11 5.2810.49 48 6.40 1 0.89 5.9610.66 6.5550.58 6.0710.10 6.9250.40 14 6.55 ; 1.49 5.6250.77 6.5150.30 7.4510.39 6.5550.66 49 7.13 i 1.19 6.3610.60 6.9650.28 7.3510.13 7.7650.61 15 6.75 i 1.03 5.9610.59 7.0350.18 7.0610.32 6.8550.50 50 7.79 ; 2.26 6.1550.25 7.7450.56 8.5250.24 8.5810.69 15 6.78 i 0.89 6.0950.66 6.9850.22 6.9710.23 7.0050.59 51 7.08 ; 1.09 6.30;0.50 7.0910.20 7.5510.23 7.3110.45 17 7.75 5 1.54 6.7410.21 7.5610.19 8.5350.20 8.0910.38 1NN 7.78 i 1.35 6.8650.41 7.6750.59 8.4110.12 8.1151.04 13 7.23 5 1.41 6.2110.38 7.1910.24 7.6450.11 7.7750.78 STATION 82 82 82 83 CODE E9V.MO. AVG. 01/06-04/06 03/31-07/02 07/08-10/08 10/08-01/18 19 6.89 ; 1.51 5.8911.03 6.8410.15 7.7250.19 7.C250.52
=- -
128 4.25 ; 3.12 2.9410.43 2.8010.23 5.3150.26 5.7850.23 20 7.8751.47 7.2350.51 7.2350.18 8.3310.41 8.6450.61 NOTE: ALL SEMICOLONS IDGICATE A PLUS OR MIP88S SIGN.
213 6.44 1 0.94 5.9310.72 6.4510.24 6.2550.09 7.0$;0.42 l
i
RMC TABLE XXV MEAN NONTHLY AND QUARTERLY TLD RESULTS FOR THE SITE BOUNDARY, MIDDLE, AND OUTER RINGS RESULTS IN UNITS OF MRAD /STD. MONTH i 2 SIGNA DEVIATION OF THE DATA.
SAMPLE EXPOSURE TYPE PERIOD B0t.NDRY MIDDLE RING OUTER RING MONTHLY JAN/82 6.73 1 2.39 7.02 1 1.77 6.52 1 1.77 FEB/82 7.89 5 2.46 8.15 1 2.06 7.86 3 2.07 HAR/82 6.% i 2.56 7.21 1 2.00 6.76 ; 1.76 APR/82 7.80 5 2.76 7.85 1 2.16 7.54 5 1.95 MAY/82 7.25 1 3.08 7.43 5 2.27 7.17 5 1.99 JUN/82 7.14 5 2.76 7.71 ; 2.09 6.78 ; 1.70 JUL/82 7.12 5 2.68 6.84 3 2.07 6.41 3 2.06 AUG/82 6.32 1 2.77 6.51 5 2.31 6.00 1 1.90 SEP/82 7.50 1 2.29 7.77 ; 1.99 7.36 5 2.41 OCT/82 7.92 ; 2.53 8.22 i 2.39 8.02 5 2.61 NOV/82 8.01 1 2.76 7.86 5 2.13 7.64 1 1.58 DEC/82 7.03 5 2.68 7.38 i 2.30 7.33 5 1.96 QUARTERLY JAN/82-APR/80 5.76 5 2.10 5.86 i 1.65 5.55 1 2.78 APR/82-JUL/82 6.44 3 2.16 6.65 1 1.90 6.16 1 3.16 JUL/82-0CT/82 6.81 & 2.92 7.02 ; 2.36 6.89 1 2.16 OCT/82-JAN/83 6.90 1 2.56 7.08 5 2.23 7.20 1 1.94 SITE BOUNDARY RING STATIONS-18, 1C, 10, IE, IF, IG, 1H, IJ, IL, 1H, IPef, 2, 40.
MIDDLE RING STATIONS
- 3A, 4K, 5, 68, 14, 15, 17, 22, 23, 26, 27, 31, 32, 33A, 38,
- 42, 43, 44, 45, 46, 47, 48, 49, 50, 51.
OUTER RING STATIONS
- 128, 16, 18, 19, 20, 21B, 24.
NOTE: ALL SEMICOLONS INDICATE A PLUS OR MIPAJS SIGN.
l s
e_--->
w a
u a
w w
r w
c v_
TABLE XXVI TYPICAL
- MINIMUM DETECTABLE LEVELS OF NUCLIDES SEARCHED FOR BUT NOT FOUND IN THE VICINITY OF PEACH BOTTOM NUCLEAR POWER STATION, 1982 NUCL IDE SURFACE WATER DISCHARGE WATER RAIN WATER AIR PARTICULATES MILK Soll (oCI/I)
(oCI/l)
(oCI/l)
(10 3 oCI/m3)
(oCI/l) foci /o-dev)
Be-7 5.5 5.7 13 11 58 0.6 Na-22 0.4 0.4 1.7 0.7 K-40 4.6 4.3 18 18 Cr-51 11 8.5 15 176 324 0.7 1.7 1.2 1.7 0.04 Mn-54 0.4 0.4 Co-57 0.8 0.3 1.2 1.5 0.03 Co-56 0.5 0.6 2.0 2.8 5.0 0.05 Fe-59 1.3 1.5 3.6 11 28 0.1 Co-60 0.4 0.5 1.7 1.6 1.9 0.05 Zn-65 0.8 1.1 3.5' 3.0 5.3 0.1 Zr-95 2.1 1.6 5.0 7.6 0.09 Nb-9) 2.8 1.3 10 14 0.08 ZrNb-95 0.5 0.5 2.7 0.8 Mo-99 168 94 622 129 157 Ru-103 2.2 1.3 7.4 11 0.07 Ru-106 3.3 3.7 16 11 15 0.4 Ag-110m 0.4 0.4 1.7 1.3 1.8 0.1 Sb-125 1.5 1.3 3.2 3.4 0.1 1
Te-129m 24 26 20 342 698 2.3 l-131 27 30 10 41 8.3 1.1 Te-132 146 5.8 59 339 l-133 136 337 Cs-134 0.4 0.4 1.7 1.0 1.3 0.04 Cs-136 8.9 5.6 5.3 19 4.6 0.2 Cs-137 0.4 0.4 1.7 1.1 0.6 0.3 Ba-140 246 46 82 1.2 La-140 77 13 24 0.3 Bala-140 2.7 2.3 5.3 3.3 Ce-141 7.2 1.8 2.5 37 0.1 Ce-144 2.7 2.2 5.3 10 15 0.3 Ra-226 2.5 0.8 2.8 15 2.5 Th-232 1.4 1.5 5.7 3.5 4.0 Np-239 540 Typical refers to mean plus two standard deviations.
Minimum detectable levels of these nuclides were not calculated for these media.
Indicates a positive concentration was measured in all samples analyzed.
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ENVIRONENTAL SAMPLING STATI(NS
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l Vill. EPA INTERLABORATORY COMPARISON PROGRAM [ [ [ [ r
SYNOPSIS OF ANALYTICAL PROCEDURES A description of analytical laboratory procedures used is provided in the following section. Also, analytics: calculation methods are described. S= ale Prenaration Eht Counting Procedures Several types of liquid samples are separated by filtration prior to analysis. Resulting portions are identified as soluble and insoluble. Therefore, soluble as used in this report, is defined as that portion of a sample that passes through a #50 Whatman filter paper. Insoluble is defined as that portion of a sample that is collected on #50 Whatman filter paper. N 4' <= o [ [ [ [ [ [ r
GROSS BETA ANALYSIS OF SAMPLES Insoluble Fraction of Water (B4) A 1000 mi aliquot of the sample is filtered through Whatman #50 filter paper. The filter paper is ashed in a preignited and preweighed 2" x 1/4" ringed planchet and reweighed. The planchet is counted in a low-background gas-flow proportional counter. Self-absorption corrections are made based on measured sample weight and calculated thickness. Sr-90-Y-90 is used as the calibration standard. A clean, unused filter paper is processed in ine same manner and used as a blank. Soluble Fraction of Water (B6) The filtrate obtained during procedure B4 is evaporated to dryness in a preweighed, 2" x 1/4" ringed planchet and rewelghed. The planchet Is counted in a low-background gasflow proportional counter. Self-absorption corrections are made based on measured sample weight and calculated thickness. Sr-90-Y-90 is used as calibration standard. An aliquot of distilled water is evaporated in the same manner and used as a blank. Calculation of results and two sigma error: bx RESULT = C(s+b) 1 1 x1 x 1-x (pCI/l) T(s+b) T(b) 2.22 E V TF 2SIGMAERROR=2/C(s+b) g 1 1x 1 b (pCI/l) V T(s+b)2, T(b)2 2.22 E V TF x x x The minimum detectable level (MOL) is defined as that value equal to the two sigma error of the result. Less than MDL is reported as the result when this value is greater than the measured result defined above. I where: C(s+b) gross counts of sanple = C(b) counts of blank = E fractional Sr-90-Y-90 counting = l efficiency T(s+b) number of minutes sample was counted = T(b) number of minutes blank was counted = V volume of aliquot (in liters) = TF transmission f actor = i
ANALYSIS OF SAMPLE FOR TRITIUM Water (H2) A 15 ml aliquot of the sample-Is vacuum distilled to eliminate dissolved gases and non-volatile matter. The distillate is frozen in a trap cooled with a dry ice-Isopropanol mixture. Eight (8) ml of the distillate are mixed with ten (10) ml of Insta-Gel liquid scintillation solution. The sample is then counted for tritium in a liquid scintillation counter. A sample of low tritium (<50 pCI/l) water is vacuum distilled as a blank and is counted with each batch of samples. In the calculation of ihe result it is assumed that the condensed and original sampie are of equiyalent volumes. The volume change associated wIth the removal of dissolved gases and non-volatile matter is not sign!ficant compared to the other errors in the analysis. Milk (H3) A 100 ml aliquot of sample is dried in a rotating vacuum flash evaporator. During the evaporation process, the evaporated water fraction is trapped out by a dry Ice-isopropanol mixture for counting. Approximately 20 ml of condensate Is vacuum distiiled to eliminate dissolved gasses and non-voiattie matter. Counting is the same as for water above. Calculation of results and two sigma error: BESULI = ' cts 49) dx 1 1 1 x x (pCl/l) , T(s+b) T(b) 2.22 E V 2[T(s+b)2+ 2 SIGMA ERROR = C(s+b) C(b) 1 1x 1 x x (pCI/I) V T(b) 2.22 E V The minimum detectable level (MDL) is defined as that value equal to the two sigma error of the result. Less than M)L is reported as the result when this ( value is greater than the measured result defined above. where: C(s+b) gross counts of sample = C(b) counts of blank = E fractional H-3 counting offIciency = T(s+b) number of minutes sample was counted = (- T(b) number of minutes blank was counted = volume of distillate counted (in liters) V = e { { r L__
ANALYSIS OF SAMPLES FOR l-131 Milk (10) The Initial stable lodide concentration in milk is determined with an Iodide specific electrode. Three milliliters of stable lodide carrier is then added to four (4) liters of milk. The lodide is removed from the milk by passage through an ion-exchange resin. The lodide is eluted from the resin with sodium hypochlorite, and purified by a series of solvent extractions with the final extraction into a toluene phase. The toluene phase is mixed with a toluene-based iIquid scintillation solution. The sample is then counted in a beta-gated gamma coincidence detector shielded by six inches of steel. Distilled water is used as a blank. The yield is calculated from stable lodide recovery based on the recovered volume. Results are corrected for decay from the sampling time to the middle of the counting period using a half-life value ) l for 1-131 of 8.06 days. Calculation of results and two sigma error: The spectrum obtained is smoothed to minimize the effects of random statistical fluctuations. The presence of lodine-131 is identified by the presence of a 364 kev peak. The net area above the baseline is calculated. This counting rate f is converted to activity (pCI) for units volume making allowance for counting effIclency and gamma ray abundance. RESULT = 'C(s+b), pdh1 1 1 1x 1x 1 x x x x (pCi/l) T(s+b) T(b) 2.22 E V Y F 1 e[.693(ti-ts)/8.06] ) =2[T(s+b)2+ 2 SIGMA ERROR C(s+b) gx 1 1x 1x 1 1x x x \\/ T(b)2 2.22 E V Y F (pCl/l) 1 e[.693(ti-ts)/8.06] f where: C(s+b) gross counts in channels containing 1-131 = peak C(b) background counts in channel containing 1-131 = peak T(s+b) number of minutes aliquot was counted = T(b) number of minutes blank was counted = E l-131 counting offIciency = V volume of allquot utilized (in liters) = Y chemical yield of iodine = F fractional gamma abundance for 1-131 = 0.824 = tl time at midpoint of the counting interval = ts time of sample collection = natural antilog e = j
Calculation of minimum detectable level 'MOL): E= 1 1x1x1x1x1x 3}6xC x x (pCl/l) 2.22 E V Y T F 1 e[.693(tI-ts)8.06] l I where: C number of counts in the channel that would have = been the centroid if a peak was there l-131 counting offIciency E = V volume of aliquot (in liters) = Y chemical yield of Iodine = T number of minues aliquot was counted = F fractional gamma abundance for 1-131 = 0.824 = time at midpoint of the counting interval tl = ts time of sample collection = natural antilog e = { [ { [ [ r
GAM SPECTROMETRY OF SAMPLES Water (N1) Four liters of sample is reduced to 100 ml and sealed in a standard container and counted with a Nal(TI) detector coupled to a multi-channel pulse-height analyzer. Milk (N7) A three liter aliquot is dried at 175 C, ashed at 500 C until no carbon residue is present, compressed and sealed in a standard container, and counted with a Nal(TI) detector coupled to a multi-channel pulse-height analyzer. Air Particulate (GB) All samples received for the month are mixed and sealed in a standard container. The container is counted with a high resolution Ge(LI) detector, coupled to a multi-channel pulse-height analyzer. Calculailon of result and two sigma error: The spectrum obtained is smoothed to minimize the effects of random statistical fluctuations. Peaks are identified by changes in the slope of the gross spectrum. The net area above the baseline is calculated. This counting rate is converted to activity in curie units making allowance for counting ef ficiency and gamma ray abundance. RESULT = 'C(s+b) _dx I 1x 1x 1 x x (pCl/v) T(s+b) T(b) 2.22 E V F 1 e[.693(ti-ts)/t1/23 2 SIGMA ERROR = J[C(s+b) I (pCi/v) V T(s+b)2 + pdh),2 1 x 1x 1x x T(b) 2.22 E-x V F 1 e[.693(ti-ts)/t1/2] where: C(s+b) gross counts in channels containing peak = of nuct Ide being quantized C(b) background counts in channels containing = peak of nuclIde being quantized T(s+b) number of minutes aliquot was counted = T(b) number of minutes blank was counted = E measured from efficiency curve fer a given = energy F fractional gamma abundance = volume of aliquot (in iIters or meters 3) V = tl time at midpoint of the counting interva' r = ts time of sample collection [ = ti/2 half-IIfe of radionuctIde = j natural antilog e =
Calculation of minimum detectable level (MDL) for Nal detectors: E= h0.63xCx I 1 1x 1x 1x x x (pCI/v) 2.22 E V F T 1 e[.693(ti-ts)/t1/23 Calculation of minimum detectable level (MDL) for GeLI detectors 3 C 1 1x 1x 1x MIL = x x (pCl/v) T 2.22 E V F 1 e[.693(ti-ts[1/23 where: C number of counts in the channel that would have = been the centroid if a peak was there E measuredfromefficiencycurveforagivenenergy = volune of aliquot utilIzed (in Iiters or meters) V = F fractional gamma abundance = T number of minutes aliquot was counted = time at midpoint of the counting interval ti = time of sample collection ts = t1/2 half-Ilfe of radionuclide = natural antilog e = ( I ( l ( [ { f
f STRONTIUM-89 AND STRONTIUM-90 ANALYSIS OF SAMPLES Milk (S4, T4) A one and half liter aliquot of milk is ashed to destroy organic material and then dissolved in concentrated mineral acid. Stable strontium is added to the eluted liquid or dissolved ash to facilitate chemical separation of Sr-89 and -90, and to determine the strontium recovery. Strontium concentrations and purification is ultimately realized by at least two precipitations of strontium nitrate in concentrated nitric acid. Additional fron/ rare earth hydroxide precipitations and barium chromate separations are performed to remove suspected interfering nuclides. After purification, the Y-90 is allowed to Ingrow for a known period of time. Sr-90 is then determined by counting yttrium oxalate af ter Initially precipitating Y-90 hydroxide. Sr-89 is determined by counting strontium carbonate and correcting the observed activity for the amount of Sr-90 and Y-90 on the planchet. A sample of distilled water is used as a blank. Calculation of result and two sigma error: RESULT Sr-90 = h_, [ x 1 1 1 1x 1 x x x (pCl/l) .T1 T2, 2.22 V E Y X 1 3(.693 t1/64.1)[j_g(.693t2/64.1)] 2 SIGMA ERROR F M = 2 A- + I 1 1 1 1x x x x x x (pCI/l) T1 12 2.22 V E Y X 1 e (.693 t1/64.1 )[j _e(.693t2/64.1 )] Gross Y-90 counts where: A = B Blank counts of yttrium = T1 Y-90 counting time = T2 Blank counting time = Sample aliquot size (in liters) V = E Y-90 counting efficiency = Y Yttrium chemical yield = Strontium chemical yield X = Time in hours from second separation of Y-90 until counting t1 = time of yttrium planchet plus one half the counting time Time in hours between fIrst and second separations of Y-90 t2 = (Ingrowth time) natural antilog ) e = The minimum detectable level (MDL) is defined as that value equal to the two sigma error of the result. Less than MDL is reported as the result when this value is greater than the measured result defined above. 1
L. 'Q_' U-G RESULT Sr-89 = 1 1 1 1x H x x x x i (pCl/v) T3; ,T4; 2.22 V F X g 1 ,(.693t4/50.5) 2 SIGMA ERROR Sr-89 2 C_ + g_ # ji-1 x1 x 1 x 'l x = x (pCI/l) T3 T4 T3 T3 2.22 Y F X 1 e(.693t4/50.5) where: C Gross strontium counts = D Blank counts of strontium = Additional background from Sr-90 activity G = (Sr-90 activity of sample) (2.22 VXJ) = Additional background from Y-90 activity H = (Sr-90 activity of sample) (2.22 VXE) [1-e(.693t5/64.1)] = V Sample aliquot size (in liters) = J Sr-90 counting officiency = F Sr-89 counting offIciency = X Strontium chemical yleld =- t4 Time in days from sampiIng date to strontium count date = T3 Strontium counting time = T4 Blank counting time = Time in hours from second separation of Y-90 to counting t5 = l of strontium planchet plus one half the counting time natural antilog e = The minimum detectable level (EL) is defined as that value equal to th': two { sigma error of the result. Less than WL is reported as the result when this value is greater than the measured result defined above. [ { { { (i l [
ENVIRONMENTAL DOSIMETRY (DO),(DI) By RMC definition, a thermoluminescent dosimeter (TLD) is considered one end of a capillary tube containing calcium sulfate (Tm) powder as the thermolumi-nescent material. This material was chosen for its characteristic high light output, minimal thermally Induced signal loss (fading), and neglIgibte setf-dosing. The energy response curve has been fIattened by a compiex multiple element energy compensator shield supplied by Panasonic Corporation, manufac-turer of the TLD reader. There exists four dosimeters per station sealed in a polyethylene bag to demonstrate Integrity at the time of measurement, and for visualization of the sample placement instructions. The zero dose is determined from TLDs located in the lead shield found at RMC, Philadelphia. Following the predesignated exposure period the TLDs are placed in the TLD reader. The reader heats the calcium sulfate (Tm) and the measured light emission (luminescence) is used to calculate the environmental radiation exposure. Data are normalized to standard machine conditions by correcting machine settings to designated values before readout. Data are also corrected for in-transit dose using a set of TLDs kept in a lead shield in the field, exposed only during transit. The average dose per exposure period, and its associated error is then calculated. A Cs-137 source is used to expose TLDs as a reference sample. An absorbed dose in tissue is determined using the 0.955 rad / Roentgen conversion factor and dose equivalent (mrem) by using a quality factor of 1. Calculation of results and two sigma error: Gross TLD (i) = [TLD(1)-D0(I)] x CF(l) x CF(Ins) x 0.955 mrad /mRoentgen ITD = Net (site 0) - [ NET (RMC 0) (D(sta) / D(RMC 0))] NET TLD(I) = gross TLD(i) - ITD AVG = [(sigma NET TLD) / n] [D(STD) / D(EX)] I=1 ERROR (95% CL) = t(n-1) [ sigma NET TLD(1) / n] [D(STD) / D(EX)] ] ) ) J
where: Gross TLD(1) Individual TLD reading corrected to standard = instrument conditions TLD(i) Gross reading of dosimeter i = NET TLD(1) Net dose obtained during exposure period in = the field CF(ins) Correction factor of reader = (6.21) (ELS-0.95) = ELS External light source = DO(l) Zero for dosimeter i = CF(l) Calibration factor for dosimeter i = ITD In-Transit dose = NET (site)0 Mean of n dosimeters in site lead shield = NET (RMC)0 Mean of n dosimeters in RMC lead shield = D(sta) Exposure period of station = O(RMC 0) Exposure period of RMC 0 = AVG Mean exposure per standard exposure period at = a given station Number of readings n = D(EX) Days exposed = D(STD) Days in standard exposure period = t(n-1) T-distribution (student) factor for 95% CL = sigma NET TDL(1) = Standard deviation of n readings of NET TLD(I) ERROR The 95% confidence Iimit error of AVG = l l { { { ( [ r
f 1 Vll. SYNOPSIS OF ANALYTICAL PROCEDURES b d Y
INTER-LABORATORY COMPARISON PROGRAM RMC participates in the EPA radiological interlaboratory 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 RMC results is obtained. Of the 98 analyses performed 91 fell within the EPA mean and standard deviation. Reference No. 3 discusses any discrepancies between the data. Tables 1-5 summarize the results of the 1982 samples. I { { l ( { [ [
TABLE 1 INTER-LABORATORY COMPARISONS GROSS ALPHA AND BETA IN WATER (pCi/ liter and AIR PARTICULATES (pC1/ filter) sat 1PLE R!lC EPA All Participants DATE RMC # TYPE ANALYSIS MEANis.d. EAN s.d. MEAN s.d. Jan 67011 Water a 2212 24 6 21 6 1982 8 2911 3215 31 6 March 70043 Water a 15 1 1915 18 4 1982 8 19 1 19 5 20 4 March 70631 APT a 24 3 27 7 26 4 1982 S 58 2 55 5 59 8 April 72020 Water a 50 3 85 21 75 16 1982 S 93 2 (a) 106 5 106 13 May 73330 Water a 22 1 28 7 25 7 1982 6 31 3 29 5 30 6 July 76747 Water a 11 2 16 5 16 5 1982 8 22 1 23 5 21 5 Sept 81226 Water a 20 1 29 7 26 6 1982 6 34 1 40 5 38 6 ) Sept 81457 APT a ?7 3 32 8 28 6 ] 1982 8 38 2 (b) 67 5 61 8 Oct 83052 Water a 48 2 55 14 47 14 1982 8 101il 81d5 76 11 Nov 84691 Water a 17 2 19 5 17 4 1982 S 22 2 24 5 24 3 ) Nov 91763 APT a 2811 27 7 29 4 1982 S 64 2 5915 66 7 ] (a) Insufficient sample to reanalyze. Probable reasons for discrepancy are incomplete transfer of sample to planchet, incormet pipetting of sample aliquot and nonhomo-3 geneity of sample. J (b) Calculation was verified. Sample could not be manalyzed because it was destroyed in the strontium analysis. Gross alpha, gamma and strontium-90 for that sanple were ] in agreement with the EPA. 1
l TABLE 2 INTER-LABORATOR{Ij0tFARIS0HS GA!MA SAffLE R!!C EPA All Participants DATE RMC i TYPE IS0 TOPE LEAN s.d. lEAH s.d. MEAH s.d. fib 68029 Water Cr-51 <56 0 59 1982 Co-60 2214 20 5 20 5 e l Zn-65 16 3 15 5 15 4 i Ru-106 <32(a) 20 5 19 8 Cs-134 20 1 22 5 21 3 Cs-137 22 0 23 5 24 4 March 70631 APT Cs-137 32 1 23 5 27 6 1982 i April 72020 Water Co-60 <3 0 5 10 1982 Cs-134 1611 15 5 15 4 l Cs-137 16 2 16 5 17 4 April 72074 tillk Co-60 3012 30 5 31 4 1982 Cs-137 28 3 28 5 30 4 Ba-140 <147 0 57 K 1530 204 1500 75 1495 178 Juns 74569 Water Cr-51 <72(b) 23 5 25 13 1982 Co-60 29 2 29 5 31 4 Zn-65 26 3 26 5 27 6 Ru-106 <30 0 10 11 Cs-134 34 1 35 5 3414 Cs-137 2412 25 5 27 4 July 76127 Food I-131 105113 94 9 10019 1982 Cs-137 2714 20 5 26 4 Ba-140 <19 0 0 K 2660 244 2400 120 2645 244 Sept 81457 APT Cs-137 25 4 27i5 25 4 1982 Oct 82539 Water Cr-51 <93 (b) 51 5 51 15 1982 Co-60 2114 20 5 20 3 e Zn-65 21 6 24 5 24 4 Ru-106 41 6 30 5 31 8 s Cs-134 16 2 1915 18 3 Cs-137 1713 2015 21 3 s V N I Y
TABLE 2 (c::nt.) INTER-LABORATORY C0! PARIS 014S GAltiA(1) SAltPLE R!iC EPA All Participants DATE BliC # TYPE ISOTOPE 14EANis.d. ItEAN s.d. liEAN s.d. Oct 83052 Water Co-60 <4 0 37 1982 Cs-134 <3 25 6 11 Cs-137 21 2 20 5 20 3 Oct 83535 !Mik I-131 47 5 42 6 40 7 1982 Cs-137 35 4 34 5 35 3 Ba-140 <31 0 25 K 1682 68 1560 78 1528 196 N:V 84177 Food I-131 30 6 25 6 25 5 1982 Cs-137 28 4 27 5 29 4 Ba-140 <32 0 0 K 2934 118 2780 140 2846 207 Nov 91763 APT Cs-137 3112 27 5 30 5 1982 (1) Results reported in pCi/ liter for milk and water, pCi/ sample for air particulates, and pC1/ kilograms for food products except K which is reported in mg/ liter for milk i and mg/ kilogram for food products. J (a) Positive activity was not detected due to the low sensitivity of the analysis for Ru-106. ) (b) Positive activity was not detected due to the low sensitivity of the analysis for ] Cr-51. ) J l
TABLE 3 INTER-LABORATORY C0ffARIS0flS TRITILE IN WATER pC1/ liter SN1PLE RitC EPA All Participants l DATE RMC # TYPE NIALYSIS lENI s.d. IEN1 s.d. IEAll s.d. Feb 67807 Water H-3 1913 138 1820 342 1853 229 1982 Apr 71295 Water H-3 2800 89 2860 360 2812i242 1982 Juns 74602 Water H-3 1867 590 1830 340 1765 229 1982 Aug 77486 Water H-3 3077 100 2890 360 2847 270 1982 Oct 82727 Water H-3 2473 58 2560 350 2517 250 1982 Dec 90744 Water H-3 2007 75 1990 345 2009 233 1982 t 1 L { f
TABLE 4 INTER-LABORATORY C0tFARIS0llS 10 DINE-131 Ill WATER pCi/ liter SNFLE R!iC EPA All Participants %TE Rt1C # TYPE NIALYSIS lEAttis. d. 14EAN s.d. ItEAf1 s.d. Jan 67243 Water I-131 7.0 0.1 8.4 1.5 8.3 1.0 1982 Apr 70963 Water I-131 66 4 62 6 63 8 1982 l Juns 75597 Water I-131 3.9 0.7 4.4 0.7 4.5 1.1 l 1982 July 77316 Water I-131 5.5 0.3 5.4 0.8 5.7 1.5 1982 Aug 78175 Water I-131 88 2 87 9 86 10 1982 Dec 90378 Water I-131 40 3 37 6 38 5 1982 ) ) ) ) ] 1 1
l TABLE 5 1 { INTER-LABORATORY C0! PARIS 0NS ) STRONTIl#1-89 NID STRONTIUll-90ll SAffLE Rf1C EPA All Participants RitC # TYPE NIALYSI' IEAN s.d. liEAN s.d. IiEAN s.d. l DATE 1 l 66079 Water Sr-89 15 1 21 5 20 4 { Jan 1982 Sr-90 12 1 12 2 11 2 March 70631 APT S r-90 28 6 (a) 16 1 16 2 1982 April 72020 Water S r-89 14 8 (a) 24 5 24 4 1982 Sr-90 10 1 12 2 12 2 April 72074 Milk Sr-89 <23 25 5 22 5 l 1982 S r-90 <26 16 2 14 3 May 73333 Water S r-89 17 2 22 5 22 5 1982 S r-90 13 2 13 2 12 2 July 76127 Food S r-89 22 11 26 5 29 7 -1982 Sr-90 18 8 20 5 23 2 Sept 80211 Water Sr-89 19 1 25 5 24 4 1982 S r-90 15 1 15 2 14 2 Sept 81457 APT S r-90 17 1 20t2 17 2 1982 Oct 83052 Water Sr-89 <5 0 13 20 / 1982 S r-90 12 1 17 2 16 2 Oct 83535 !! ilk S r-89 <5 0 33 1982 S r-90 17 1 19 2 17 3 Nov 84177 Food S r-89 16 2 0 7 13 1982 Sr-90 22 17 28 2 26 7 Nov 91763 APT Sr-90 16 1 16 2 16 2 1982 (1) Results reported in pC1/1 for water and milk, pCi/ filter for air particulates, and pCi/kg for food. (a) A new strontium procedure was introduced in liarch 1982. .hese interconparison sam-ples were analyzed in the testing stage and showed the need for retraining in sepa-ration technique. f _ - - _ _ _}}