Text

Gpu Nuclear Corp Oyster Creek Nuclear Generating Station Effluent Release Rept,June-Dec 1982
	ML20069A849
Person / Time
Site:	Oyster Creek
Issue date:	03/16/1983
From:	; GENERAL PUBLIC UTILITIES CORP.
To:	;
Shared Package
ML20069A853	List: ML20069A849;
References
	10CFR-050.36A, 10CFR-50.36A, NUDOCS 8303160309
	Download: ML20069A849 (197)
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GPU NUCLEAR CORPORATION OYSTER CREEK NUCLEAR GENERATING STATION EFFLUENT RELEASE REPORT 1982-2 f

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SUMMARY

OYSTER CREEK NUCLEAR GENERATING STATION 1982-2 SEMIANNUAL EFFLUENT RELEASE REPORT The Semiannual Effluent Release Report is submitted to the United States Nuclear Regulatory Commission (NRC) every six months'in accordance with the Oyster Creek Nuclear Generating Station (OCNGS) Technical Specifications. It summarizes the radioactive liquid and gaseous effluents released and solid radioactive wastes shipped from the OCNGS.

In addition, it describes the results of environmental measurements undertaken to determine the effects of such radioactive releases to the environment. Samples were collected of environmental media such as air, sediment, surface water, well water, soil, precipitation, vegetation, and shellfish. These media are sampled on a routine basis at semimonthly, monthly and/or quarterly frequencies at 37 locations. The annual magnitude of effort to collect and analyze the environmental samples is in excess of four man years at a cost exceeding $200,000.00. This report concludes that exposures to man from OCNGS radioactive effluents are well below the federal limits contained in Title 10, Part 50 of the Code of Federal Regulations and are considered by the NRC to be within acceptable limits in protecting the health and welfare of the public.

For clarity, the report is organized into three parts.Section I provides a summary of plant operations for the reporting period. OCNGS operated appecximately 191 days between June through December.

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Section II summarizes the meteorological data and effluents released 4

from the facility.

It itemizes stack releases of 1.07 x 10 curies of fission and activation gases, 4.74 curies of Tritium, 2.17 curies of

-1 non-particulate halogens, and 5.72 x 10 curies of particulates.

In

-4 addition, 1.26 x 10 curies of fission and activation products, 5.61 x

-3 10 curies of dissolved gases, and 1.05 curies of Tritium were released in 5 batch liquid releases.Section II also itemizes 1.29 x 3

10 curies of radioactivity contained in 552 cubic meters of waste 2

shipped offsite in 49 shipments, as well as 4.53 x 10 curies of radioactivity contained in 17 cubic meters of irradiated material which were shipped offsite in 6 shipments. These releases are similar to or less than releases of nuclear plants of comparable type, age, and size.

The report underscores the fact that all effluents released were within the federal regulatory requirements of OCNGS Technical Specifications.

Section III summarizes the results of the Radiological Environmental Monitoring Program (REMP). This section concludes that no radioactive levels in the environment were attributable to facility operations for the reporting period. Natural radioactivity and weapon testing fallout were considered the causes of slightly higher than background readings, where detected. All levels of radioactivity in the environment fall well within the acceptable levels considered by the NRC to safeguard the health and welfare of the general public.

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TABLE OF CONTENTS' PAGC LIST OF TABLES i

LIST OF FIGURES iii l

I INTRODUCTION 1

II EFFLUENT AND WASTE DISPOSAL

SUMMARY

5 III RADIOLOGICAL ENVIRONMENTAL

SUMMARY

44 IV REFERENCES 189 l

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4 LIST OF TABLES Table i Title Page Table 1 Effluent and Waste Disposal Semiannual Report 13 1982-2.

Gasecus Effluents - Summation of all Releases.

Table 2 Effluent and Waste Disposal Semiannual Report 14 1982-2.

Gaseous Effluents - Elevated Release, Fission gases and iodines.

Table 3 Effluent and Waste Disposal Semiannual Report 15 1982-2.

Gaseous Effluents - Elevated Release, other radionuclides.

Table 4 Effluent and Waste Disposal Semiannual Report 16 1982-2.

Gaseous Effluents - Ground Level Releases.

Table 5 Effluent and Waste Disposal Semiannual Report 17 1982-2.

Liquid Effluents - Summation of all Releases.

Table 6 Effluent and Waste Disposal Semiannual Report 18 1982-2, Liquid Effluents.

Table 7 Effluent and Waste Disposal Semiannual Report 19 1982-2.

Solid Waste and Irradiated Fuel Shipments.

Table 8 Meteorological Classifications of Atmospheric 24 Stability.

Table 9 Oyster Creek Joint Frequency Tables of Wind 25-28 Speed and Direction (33 feet) versus Delta Temperature (150-33 feet).

7/1/82 - 9/30/82 Table 10 Oyster Creek Joint Frequency Tables of Wind 29-32 Speed and Direction (33 feet) versus Delta Temperature (150-33 feet). 10/1/82 - 12/31/82 Table 11 Oyster Creek Joint Frequency Tables of Wind 33-36 Speed and Direction (380 feet) versus Delta Temperature (380-33 feet). 7/1/82 - 9/30/82 t

Table 12 Oyster Creek Joint Frequency Tables of Wind 37-40 Speed and Direction (380 feet) versus Delta Temperature (380-33 feet).

10/1/82 - 12/31/82

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i LIST OF TABLES Table 4 Title Page Table 13 Average Meteorological Data Recovery for 41 the Oyster Creek Nuclear Generating Station Table 14 Oyster Creek Station - Environmental 48-51 honitoring Stations - Location and Sample Type Collected.

Table 15 Radiogas Film Badge

Exposures -

54 June 1, 1982 through November 30, 1982 Table 16 Direct Radiation (ER) as measured by 55 Thermoluminescent Dosimeter - June 1, 1982 through November 30, 1982.

Table 17 Radiological Environmental Monitoring 56 Program Format Summary Table 18 REMP Semiannual Sumnary -

57-113 June 1, 1982 through November 30, 1982 1

Table 19 REMP First Quarter Summary -

114-147 June 1, 1982 through August 31, 1982 Table 20 REMP Second Quarter Summary -

148-179 September 1, 1982 through November 30, 1982 Table 21 Summary of Maximum Individual Doses for the period 186 from July 1, 1982 through September 30, 1982 Table 22 Summary of Maximum Individual Doses for the period 187 from October 1, 1982 through December 31, 1982 Table 23 Summary of Maximum Individual Deses for the period 188 from July 1, 1982 through December 31, 1982 i

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LIST OF FIGURES Fiqure 8 Title Page 1

Meteorological Data: Schematic Diagram of System Components and Information Flow 23 2

Wind Rose - 33' Level - July 1982 through December, 1982 42 3

Wind Rose - 380' Level - July,1982 through December 1982 43 4

Map of Operational Environmental Survey Indicator Stations 52 5

Map of Operacional Environmental Survey Indicator and Background Stations 53 s

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I.

INTRODUCTION,

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INTRODUCTION The Oys!

'teek Nuclear Generating Station has generated electricity since De: ember, 1969. The operating license permits l

l station operation up to a power level of 1930 megawatts (thermal) at a levelized, installed annual capacity of 620 megawatts (electrical). A more detailed description of the facility can be obtained from the Final Environmental Statement.

This report is submitted in accordance with Section 6.9.3 of the Technical Specifications - Appendix A of the Oyster Creek Unit Number 1 Provisional Operating License, DPR-16.

Section I includes a brief summary of the plant status from June 1,1982 through December 31, 1982. This summary reports dates of reactor scrams, controlled reactor shutdowns, reactor startups, and selected reactor power 1

levels.

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Section II follows the format of USNRC Regulatory Guide 1.21 for the provision of summaries of OCNGS gaseous effluents, liquid effluents and solid waste offsite shipments. In addition, this section provides information on meteorological data for the reporting period of July 1, 1982 through December 31, 1982. A description of the meteorological data collection system is provided, as well as joint frequency distribution tables for the various stability classes (in USNRC Regulatory Guide 1.21 fornat) and cumulative wind roses.

Section III provides a summary of the Oyster Creek Radiological Environmental Monitoring Program and its associated sampling data for the reporting period of June 1, 1982 through November ?C, 1982 as i L

1 required by section 4.6.B(3) of the Technical Specifications -

Appendix A.

Radiological Environmental data are presented as recommended in proposed USNRC Regulatory Guide 4.8.

This section also correlates plant effluent releases to radiological environmental data.

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PLANT OPERATIONS

SUMMARY

June 1, 1982 Operating at Approximately 63% Rated Power June 4, 1982 Reactor Scram June 5, 1982 Reactor Startup June 15, 1982 Operating at Approximately 76% Rated Power June 30, 1982 Operating at Approximately 75% Rated Power July 15, 1982 Operating at Approximately 69% Rated Power July 31, 1982 0?erating at Approximately 65% Rated Power August 15, 1982 Reactor Shutdown August 29, 1982 Reactor Startup August 31, 1982 Operating at Approximately 69% Rated Power September 15, 1982 Operating at Approximately 60% Rated Power September 30, 1982 Operating at Approximately 56% Rated Power October 15, 1982 Operating at Approximately 53% Rated Power October 31, 1982 Operating at Approximately 50% Rated Power November 15, 1982 Operating at Approximately 47% Rated Power November 30, 1982 Operating at Approximately 44% Rated Power December 10, 1982 Reactor Shutdown December 20, 1982 P.eactor Startup December 31, 1982 Operating at Approximately 41% Rated Power,

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II.

EFFLUENT AND WASTE DISPOSAL

SUMMARY

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4.

EFFtUENT AND WASTE DISPOSAL

SUMMARY

A.

Gaseous Effluents During the reporting period, July 1, 1982 through December 31, 1982, a total of 1.07 E4 curies of fission and activation gases, 1.46 E-1 curies of non-particulate halogens (iodines) with half-lives greater than eignt days, 5.30 E-2 curies of particulates with half-lives greater than eight days, and 4.74 curies of tritium were released. Totals include effluents released from both the elevated stack and the ground-level radwaste vent. The maximum hourly release rate of gross activity from the stack was 4.16 E3 microcuries per second which occurred at approximately 1300 hours0.015 days 0.361 hours 0.00215 weeks 4.9465e-4 months on July 26, 1982.

The airborne releases are summarized in Tables 1 through 4.

B.

Liquid Effluents A total of 2.11 E7 liters of water was processed throug'h the radwaste system. Of this, 3.58 E5 liters containing 1.05 curies of activity were released to the environment. The maximum concentration of gross radioactivity (beta-gamma) released to the unrestricted area (average over the period of release) was 3.29 E-8 microcuries per milliliter on October 10, 1982. The liquid releases are summarized in Tables 5 and 6.

C.

Solid During the reporting period, a total volume of 5.69 E2 cubic meters of solid waste containing 1.75 E3 curies of activity was shipped off site in 55 shipments. No irradiated fuel was shipped.

The solid waste shipments are summarized in Table 7.

f D.

Meteorological Data During the reporting period, onsite meteorological cond'itions were monitored and recorded. Joint frequency distribution of 116 meter (380 feet) and 10 meter (33 feet) wind speed and direction per 4

atmospheric stability class per quarter is s'mmarized. Also included u

are cumulative wind roses for 10 meter (33 feet) and 116 meter (380 feet). The meteorological data are summarized in Tables 8 through 13.

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EFFLUENT AND WASTE DISPOSAL SEMIANNUAL REPORT SUPPLEMENTAL INFORMATION FACILITY - Oyster Creek Nuclear Generating Station LICENSEE - Jersey Central Power & Light Company 1.

Regulatory Limits a.

Fission and Activation Gases:

Technical Specification 3.6.A.1 Q = 0.21__ Ci/sec E

b.

Iodines and particulates, halflives )>8 days:

Technical Specification 3.6.A2 4 uCi/sec c.

Liquid Effluents:

Technical Specification 3.6.B.1 Maximum permissible concentrations, Appendix B, Table II, Column 2 of 10 CFR 20.

2.

Maximum Permissible Concentrations (MFC) a.

Fission and Activation Gases:

1.

Third Quarter - 2.80 E-3 uCi/cc 2.

Fourth Quarter - 2.93 E-3 uCi/cc b.

Iodines and Particulates:

1.

Third Quarter - 4.21 E-8 uCi/cc 2.

Fourth Quarter - 4.21 E-8 uCi/cc.. - - -

c.

Liquid Effluents:

'From Appendix B, Table II, Column 2, of 10 CFR 20-(NOTE: MPC's for isotopes detected listed below)

Unit - uCi/ml H-3 3 E-3 Co-60 5 E-5 St-89 3 E-6 Xe-133 3 E-6 Xe-135 3 E-6 Cs-137 2 E-5 Ce-143 4 E-5 3.

Average Energy a.

Third Quarter - 7.77 E-1 MeV b.

Fourth Quarter - 7.55 E-1 MeV 4.

Measurements and Approximation of Total Radioactivity a.

Fission and Activation Gases:

The incorporation of a weekly grab sample analysis using gamma ray spectrometry with a GeLi Detector, a conversion factor and the continuous recording of the stack effluent on a continuous activity monitor.

b.

Iodines Semi-weekly sample analysis using gamma ray spectrometry with a GeLi Detector.

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c.

Particulates:

Semi-weekly sample analysis using gamma ray spectrometry with a GeLi Detector, low background beta counter, internal proportional beta counter,'and a single channel gamma counter.

d.

Liquid Effluents:

Analysis per batch release using gamma ray spectrometry with a GeLi Detector, a low background beta counter, and a liquid scintillation counter.

Analysis of Error Associated with the Measurement of Radioactive Materials in Effluents and Solid Wastes Effluents All stages of the production of effluent estimates have been assigned an upwardly conservative error potential. Stages include sample collection, radiochemical analysis, and compilation of the effluent estimation process. The use of these error factors assures that facility effluents will not be underestimated.

1 Solid Wacte The process by which the levels of radioactive materials in solid wastes are estimated is one which requires conservatism throughout.

Representative sample analyses and/or surface contamination surveys are combined with estimates of waste volume to provide the level of radioactive materials in sol.d wastes. Upwardly conservative techniques are used in all phases of this process to assure that the amount of radioactive material in solid wastes are not underestimated.

5.

Batch Releases a.

Liquid 1.

Number of batch releases:

a.

Third Quarter - 4 releases b.

Fourth Quarter - 1 release 2.

Total time period for batch releases:

a.

Third Quarter - 4.97 E2 minutes b.

Fourth Quarter - 2.70 E2 minutes 3.

Maximum time period for a batch release:

a.

Third Quarter - 1.40 E2 minutes b.

Fourth Quarter - 2.70 E2 minutes 4.

Average time period for a batch release:

a.

Third Quarter - 1.24 E2 minutes b.

Fourth Quarter - 2.70 E2 minutes 5.

Minimum time period for a batch release:

a.

Third Quarter - 1.05 E2 minutes b.

Fourth Quarter - 2.70 E2 minutes 6.

Average stream flow during periods of release of effluent in a flowing stream:

a.

Third Quarter - 2.75 E6 liters / minute b.

Fourth Quarter - 2.38 E6 liters / minute i

6.

Abnormal Releases a.

Liquid 1.

Number of releases:

None 2.

Total activity released:

Not Applicable b.

Gaseous 1.

Number of releases:

None 2.

Total activity released:

Not Applicable

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TABIE 1 EFFIENT AND WASTE DISPOSAL SEMIANNUAL REPORT 1982-2 GASEQUS EFFIENIS-SIMRTICE OF ALL RELEASES Third Fourth Est. Total Unit Quar ^er Quarter Error %

A. Fission & activation gases

l. Total release Ci 3.7C E3 7.04 E3 3.0 El

2. Average release rate for period uCi/sec 5.47 E2 9.93 E2 1

3. Percent of Tech Spec limit 2.03 E-1 3.57 E-1 B. Iodines

1. '1btal iodine-131 Ci 1.07 E-1 3.86 E-2 2.5 El

2. Average release rate for period uCi/sec 1.34 E-2 4.85 E-3 f

3. Percent of '.%ch Spec limit 4.51 E-1*

1.72 E-l*

C. Particulates 1* Phdates M Ci l'.62 E-2 2.5 El half-lives >8' days 3.68 E-2

2. Average release rate for period pCi/sec 4.63 E-3 2.04 E-3

3. Percent of Tech Spec limi.t 4.51 E-l*

1.72 E-1*

4. Gross alpha radioactivity Ci 9.l? E-6 5.45 E-6 D. Tritium

1. 'Ibtal release Ci 2.26 2.48 4.0 El

2. Average release rate for period pCi/sec 2.84 E-1 3.12 E-1

Percent of Tech. Spec. Limit for Iodines and Particulates as Required t

by Technical Specification 3.6.A.2

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TABLE 2 EFFLUmT AND NASIE DISPOSAL SD1IANNUAL REPORP 1982-2 GASEDUS EFFIDENTS-EIEVA'IED RELEASE CCNTINDOUS FDDE fhird Fourth Niv-1 Maa 91eanad Unit Quarter Quarter uCi cc

1. Fission gases krypton-85m Ci 1.33 E2 3.76 E2 3.32 E-8 krypton-87 Ci 3.72 E2 1.16 E3 1.81 E-7 krypton-88 Ci 6.63 E2 1.13 E3 9.35 E-8 xenon-133 Ci 6.52 El 1.97 E2 5.65 E-8 xenon-135 Ci 7.17 E2 2.54 E3 1.I2 E-7 xenon-135m Ci 3.72 E2 3.60 E2 1.65 E-7 XE:non-138 Ci 1.20 E3 1.28 E3 7.04 E-7 others kivviisu-89 Ci (MDL 8.19 E-4 1.65 E-6 xenan-133m Ci

( MDL

< MDL 2.10 E-7 xenan-137 Ci i_gi 79 s,,

y_,

2.91 E-6

'Ibtal for period Ci 3.68 E3 7.04 E3

2. Iodines Iodine-131 Ci 1.07 E-1 3.86 E-2 2.29 E-13 Iodine-133 Ci 5.69 E-1 2.05 E-1 5.64 E-13 Iodine-135 Ci 9.48 E-1 3.01 E-1 5.25 E-12 Total for period Ci 1.62 5.45 E-1

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TABLE 3 EFFLUENT AND WASTE DISP 0FAL SEMIANNUAL REPORT 1982-2 GASEOUS EFFLUENTS - ELEVATED RELEASE Third Fourth MDL Nuclides Released Unit Quarter Quarter uCi/cc 3.

PARTICULATES Strontium-89 C1 7.80 E-3 2.81 E-3 8.37 E-15 Strontium-90 Ci 7.49 E-5 5.37 E-5 1.86 E-15 Cesium-134 Ci 7.71 E-5 (MDL 2.60 E-13 Cesium-137 C1 3.30 E-4 4.75 E-5 2.82 E-13 Barium-140 C1 2.11 E-2 9.32 E-3 1.26 E-12 Lanthanum-140 C1 1.69 E-2 8.50 E-3 4.78 E-13 OTHERS Chromium-51 Ci (MDL 1.39 E-4 1.45 E-12 Manganese-54 Ci 3.01 E-3 1.62 E-3 4.10 E-13 Cobalt-58 C1 2.43 E-4 1.45 E-4 4.12 E-13 Iron-59 C1 3.94 E-4 2.11 E-4 7.27 E-13 Cobalt-60 C1 2.61 E-4 2.68 E-4 4.29,E-13 Strontium-91 Ci 1.71 E-1 1.28 E-1 1.68 E-12 Niobium-95 Ci 5.80 E-5 (MDL 4.12 E-13 Technetium-99m C1 1.81 E-2 3.20 E-3 5.24 E-13 Iodine-131 Ci 3.18 E-3 1.27 E-3 1.55 E-13 Iodine-133 C1 4.11 E-2 1.41 E-2 3.53 E-13 Iodine-135 Ci 9.43 E-2 2.43 E-2 3.14 E-12 i

Cerium-141 C1 1.25 E-4 2.14 E-4 5.62 E-13 Cerium-144 Ci 9.94 E-5 8.66 E-5 2.88 E-12 Neptunium-239 C1 1.01 E-4

( MDL 3.88 E-13 TOTAL Ci 3.78 E-1 1.94 E-1 l,

)

NO OTHER NUCLIDES IDENTIFII:D.

l' TABLE 4 EFFLUENT AND WASTE DISPOSAL SEMIANNUAL REPORT 1982-2 GASEOUS EFFLUENTS - GROUND LEVEL RELEASES Third Fourth MDL l

Nuclides Released Unit Quarter Quarter uCi/cc 1.

Fission Cases TOTAL C1 1.74 El

( MDL 2.

Iodines Iodine-131 Ci 5.39 E-6 1.23 E-6 3.89 E-13 Iodine-133 C1 2.04 E-5 3.84 E-6 4.68 E-14 TOTAL Ci 2.58 E-5 5.07 E-6 3.

Particulates Manganese-54 C1

( MDL 6.24 E-8 8.84 E-14 Cobalt-57 Ci 3.67 E-8 3.22 E-8 1.04 E-14 i

Cobalt-60 Ci 9.55 E-7 2.09 E-6 8.63 E-14 Strontium-89 Ci,

1.04 E-8 MDL 6.79 E-16 Strontium-90 C1

( MDL MDL 4.46 E-16 Molybdenum-99 Ci 5.61 E-7

( MDL 4.17 E-13 Technetium-99m Ci 3.83 E-6 1.74 E-7 5.41 E-14 Cesium-137 C1 2.17 E-7 9.98 E-7 5.98 E-14 Cerium-141 Ci 9.84 E-8 5.58 E-8 5.37 E-14 1

Neptunium-239 C1 1.70 E-7 1.26 E-7 4.19 E-14 5

TOTAL Ci 5.88 E-6 3.54 E-6 l

NO OTHER NUCLIDES IDENTIFIER TABLE 5 EFFIDENT AND WASTE DISPOSAL SH4IANNUAL REPOIU 1982-2 LICUID EFFIUSTS-SGNATION OF ALL RELEASES Third Fourth Est. Total Unit Quarter Quarter Error %

A. Fission and activatim products

1. 'Ibtal releases (not including d

tritium, cases, aloha) 1.05 E-4 2.05 E-5 3.0 El

2. Average diluted ccmcentration uCi/ml 9.33 E-13 1.75 E-13 a374no nov4na

3. Per nt of applicable limit 3.54 E-6 4.85 E-7 B. Tritiun

1. Total release Ci 8 44 E-1 2.05 E-1 3.0 El

2. Average diluted concentration uCi/ml 7.50 E-9 1.75 E-9 durina opriod

3. Percent of applicable limit 2.50 E-4 5.84 E-5 C. Dissolved and entrained gases

1. Total release Ci (MDL 5.61 E-3 3.0 El

2. Average diluted concentration pCi M 4.79 E-11 durina Deriod

3. Percent of applicable limit 1.60 E-3 1

D. Gross alpha radioactivity

1. Total release Ci 9.73 E-6 (MDL 3.0 El E. Volune of waste ralaaW liters (erinr to dilution) 2.88 E5, 7.00 E4 1.0 El 1

F. Volume of dilution water h liters 4.23 E11 4.40 Ell 1.0 El anr,nc nor,nd L -.

TABLE 6 EFFLUENT AND WASTE DISPOSAL SEMIANNUAL REPORT 1982-2 LIQUID EFFLUENTS Third Fourth MDL Nuclides Released Unit Quarter Quarter uCi/ml Cobalt-60 Ci 5.66 E-5 2.00 E-5 5.17 E-7 Strontium-89 C1 3.23 E-6 5.03 E-7 3.91 E-9 Strontium-90 C1

( MDL

( MDL 3.15 E-9 Cesium-137 C1 2.55 E-5

( MDL 6.68 E-7 Cerium-143 C1 1.97 E-5

( MDL 7.85 E-7 l

r l

0 Total C1 1.05 E-4 2.05 E-5 i

Xenon-133 Ci

( MDL 9.38 E-4 5.30 E-7 1

Xenon-135 Ci

< MDL 4.67 E-3 3.15 E-7 Total C1

( MDL 5.61 E-3

) i

l TABLE 7 EETIENT AND WASTE DISPOSAL SEMIANNUAL REPORT 1982-2 SOLID WASTE AND IRRADIATED FUEL SHIPMENTS A. Solid waste shipped offsite for burial or disposal (not irradiated fuel) 6-nonth Est. 'Ibtal

1. Type of waste Unit mriod Error, %

a. Spent resins, filter sludges, m3 1.50 Ez

.ummen ene kn*+,,n. _. *,.

eq 1.27 E3 5.0 El j

b. DryC.wyressible waste mJ 4.02 E2 conemninated eanin., etc.

Ci 2.49 El 5.0 El d

c. Irradiated otmponents, ccntrol m

1.70 El mela. aer-c'i 4.51 F2 5.O F1 m3

d. Other (describe )

ci

2. Estimate of major nuclide ccmposition Percentage Activity (Ci)

MDL (by tvoe of wante) uCi/ml

a. Cobalt-60 6.18 El 7.85 E2 7.35 E-4 Manganese-54 1.48 El 1.88 E2 7.35 E-4 Cesium-137 9.22 1.17 E2 3.97 E-4 Strontium-89 2.17 2.76 El 1.12 E-8 Lanthanum-140 2.08 2.64 El 7.73 E-4

b. Cobalt-60 6.81 El 1.70 El Cesium-137 1.20 El 2.99 Manganese-54 9.31 2.32 Cesium-134 2.09 5.20 E-1 Zine-65 1.09 2.71 E-1

c. Antimony-125 6.07 El 2.75 E2 Cobalt-60 3.93 El 1.78 E2 l

d.

l

3. Solid Waste Disposition Mode of Transportation Destination

% gf g g

55 MOTOR VEHICLE BARhVELL. SC 1

B. Irradiated Ebel Shipments (Disposition)

Nunber of Shipments Mode of Transportation Destination l

None 1

1 )

Meteorological Data Abstract The Oyster Creek Nuclear Generating Station obtains meteorological data from the Forked River meteorological instrument tower. The tower is 400 feet tall and located approximately west-northwest of the site at a distance of 2529 feet from the stack. The following instrumentation is located on the tower:

HEIGHT OF INSTRUMENT INSTRUMENT ABOVE GROUND (feet) i 33 Wind Speed Wind Direction Temperature Dew Point 150 Wind Speed Wind Direction Temperature 380 Wind Speed Wind Direction Temperature Dew Point There are redundant wind speed, wind direction, and temperature 4

sensors at the 33 and 380 foot levels to insure an efficient amount of data recovery and to comply with regulatory requirements.

In addition, a O

processor calculates temperature differentials (thT) between (150-33)-

and (380-33)-foot levels. These data are then stored in the on-site computet and are used to determine atmospheric stability and, in turn, atmospheric dispersion. Some of the previously mentioned parameters are also monitored at the Oyster Creek Control Room (380' level wind speed and direction, and the 380'-33' ZiT).

The meteorological tower sensors, chart recorders, and processors are calibrated four times a year, according to the proposed U.S. Nuclear Regulatory Commission Regulatory Guide 1.23.

Periodic tower inspections are done to insure maximum data integrity. Table 13 shows the monthly Oyster Creek Meteorological Tower data recovery for the six month period from July through December of 1982. Meteoro' logical data are an integral part of the off-site dose assessment program. Occasionally lower percentages of data recovery, as in the month of September, are the result of sensor, computer hardware, and chart recorder malfunctions.

Data Analysis Tables 9 through 12 are the joint frequency distribution tables for the various stability classes as described in U.S. Nuclear Regulatory Commission Reg. Goide 1.21.

These atmospheric stability classes are defined in Table 8.

Joint frequency tables are represented in Figures 2 and 3 as cumulative semi-annual wind roses. Figures 2 and 3 represent wind roses at the 33-foot and 380-foot levels, respectively. The predominant wind directions are from the northwest, west, and southwest.

According to Critchfield (1974) the reason for the diversity of wind directions is a result of changing seasonal heat budget at different -- -.

latitudes. During the summer season, the prevailing winds are generally

^

from the southwest.

In late fall and winter the prevailing winds are generally from the west and northwest. Obviously, with a large representative data set over such a relatively long period of time, any relatively small weather feature producing infrequent wind directions such as sea breezes and extratropical storms will fail to appear in the cumulative six-month wind roses. For example, the common daytime summer seabreeze creates an easterly wind with high atmospheric stability and thereby surpresses major effluent plume dispersion. This thermally-induced phenomenon disappears at night and ushers the return of normal climatologically prevailing winds.

Precipitation for the period was below normal (12.24 inches). Normal 6-month rainfall is about 21 inches. Rainfall events were primarily due to extratropical storms of light to medium intensity and long duration or violent convective uplift in the form of showers and thunderstorms. This condition is characteristic of heavy rainfall intensity of relatively short duration. Generally, the heavier the intensity (convective showers) the greater the particulate fallout (washout) from the atmosphere which has implications for radionuclide deposition. Such convective showers are characteristic of late spring and summer weather patterns. Surpression of these summer precipitation events so close to the ocean is accomplished by the previously mentioned seabreeze effect.

y It is common for the showers to build up to the west, move east-northeast, but become stagnant and eventually decay up to 12 miles p

inland due to the highly stable seabreeze..

FIGURE 1 GPU NUCLEAR CORPORATION OYSTER CREEK NUCLEAR GENERATING STATION METEOROLOGICAL DATA:

SCllEMATIC DIAGRAM

_sa-rmt Ltvrt OF SYSTEM COMPONENTS AND INFORMATION FLOW K

D.G.I MAIN COMPUTER FOR STORAGE OF ME~iEOROLOGICAL DATA AT DIGITAL GRAPHICS, INC.,

d L WASHINGTON, D. C.

i r p(REMOTE}

REMOTE ACCESS:

0.C. ENVIRONMENTAL CONTROLS COMPUTER TERMINAL

_tse-FOOT LtVEL OCNGS SELECTED STRIP CIIART s

RECORDERS IN Tile OCNGS CONTROL ROOM

_3s-root LEvtt i.OrPUTER p

400' METEOROLOGICAL TOWER WITil INSTRUMENT TRANSMITTERS AT 3 LEVELS, SIGNAL PROCESSORS, COMPUTER, AND ALL STRIP CllART RECORDERS AT BASE TABLE 8 METEOROLOGICAL CLASSIFICATION OF ATMOSPHERIC STABILITY Stability Pasquill 08 Temperature Change Classification Categories (degrees)

With Height (*F/100 ft)

Extremely Unstable A

25.0

-1.0 Moderately Unstable B

20.0

-1.0 to -0.9 Slightly Unstable C

15.0

-0.9 to -0.8 Neutral D

10.0

-0.8 to -0.3 Slightly Stable E

5.0

-0.3 to 0.8 Moderately Stable.

F 2.5 0.8 to 2.2 Extremely Stable G

1.7 2.2 1

Standard deviation of horizontal wind direction fluctuation over a period of 15 minutes to 1 hour1.157407e-5 days 2.777778e-4 hours 1.653439e-6 weeks 3.805e-7 months . The values shown are average for each stability classification.

t 4 '

TABLE 9 Oyster Creek Meteorological Tower Joint Frequency Tables of Wind Speed and Wind. Direction 33ft versus Delta Temperature 150-33ft for the Period 7/1/82 - 9/30/82 siiE. DvstER CREES er/14/es is.sr

$1TE. ovsTER CREEK

.2/f4/05 is.fB HOURS.At EACH vlND sPEE0 ANO DIREC180N HOURS AT.E.ACH vlN.O SPEED AND DIRECTION 2 7eiei-2 858;t4 PERIDO OF RECORO =

82 7 181-82 5 24 PERIOD OF RECORD =

51Aell:17 CLASS, A

OT/02 STA83Liff CLASS.

e OT/D2

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e TABLE 10 Oyster Creek Meteorological Tower Joint Frequency Tables of Wind Speed and Wind Direction 33ft versus Delta Temperature 150-33ft for the Period 10/1/82 - 12/31/82 Slit. OYSTER CREER SITE. DVSTER CREEK HOURS AT EACH WlHO SPEED AND dlRECil0N HOURS AT EACH WIND SPEED ANO DIRECTION PERIOD OF PECORO.

02800181-82125124 PERIOD OF pfCORO =

32190181-02125124 ST ASILITV LLA55.

A 01/02 STASILITY CLASS.

8 DT/DZ LAPSE.Dil58 ELEVAllON.-.-....-...-... SPEED.SPD55A

-...-......-...----. ION.DIR55A LAPSE.DTI5S

..............................IRECil0N.D.IR55A DIRECT ELEVAi!ON, SPEED.5P055A D......-.. -.=

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

WIND $PEEDff' PHI WIPO SPEEDif1 PHI WlHO WINO 47 0-12 15-18 10 24

24 TOTAL DIRECTION l.3 47 0.l2. 15-18 10-24 324 TOTAL DIRECT 10M

.l..3 N

2 is IS 2

0 0

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8 8

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TOTAL 24 474 252 40 2

8 500 TOTAL I4 27 IO ll 0

0 71

.........................._,__=_

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PERIODS OF CALfifHOURSI e i

PERl005 0F CAttilHOURSI.

I WARI AetE DIRECTION 6

VARIA8tE DIRECilON S

HOURS OF filSSING DATAe de HOURS OF fil5 SING 0.41A.

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TABLE 10 (Continued)

SITE. OTSTER CREEg 02/14/03 18.22 SITE. OTSTER CREER 92/84/05 15.22 HOURS AT EACH WINO SPEE0 ANO DIRECil0N HOURS AT EACel VINO SPEE0 AND DIRECTION PERIOD OF RECORO =

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S218e181-92523124 STABILITY CLASS.

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SPEED.SP055A DIRECTION.DIR33A LAPSE.Dil88 ELEVAff0N.

SPEED.SP035A OIRECTION.DIRISA LAPSE 01158

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9 382 TOTAL 430 074 579 139 28 8 2150

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SITE. Dvsttp CREEn st/84/e5 15.41 EITE. Ov$tER CREEE 82/84/e5 15.42 HOURS AT EACH WIND SPEED AND DIRECTION HOURS AT EACH WINO SPEED AND DIRECTION PtRIOo 0F RECORo.

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s TABLE 13 AVERAGE METEOROLOGICAL DATA RECOVERY PERCENTAGE l

l FOR THE OYSTER CREEK NUCLEAR GENERATING STATION METEOROLOGICAL TOWER i

MONTH RECOVERY l

(%)

JUL 82 96 l

I AUG 82 97 l

SEP 82 82 OCT 82 98 NOV 82 96 DEC 82 96 I

i

FIGURE 2 GPU NUCLEAR CORPORATION OYSTER CREEK NUCLEAR GENERATING STATION JULY 1982 - DECEMBER 1982 (33' LEVEL)

IE 4

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FIGURE 3 l

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r 12 2

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RADIOLOGICAL ENVIRONMENTAL

SUMMARY

SECTION III - RADIOLOGICAL ENVIRONMENTAL

SUMMARY

Radiological Environmental Monitoring Program Introduction The Radiological Environmental Monitoring Program was conducted during the reporting period in accordance with Technical Specification 4.6.B.3.

The Technical Specifications, which refer to the Application for Reactor License, Docket No. 50-219, Amendment No.

65, require five general types of monitoring:

(1) a tmospheric radiation, (2) fallout, (3) domestic water, (4) surface water, and (5) marine life. This monitoring was accomplished by collecting samples f rom the var ious environmental media at sample collection stations as outlined in Table 14 and Figures 4 and 5.

Specifically, film badges and thermoluminescent dosimeters (TLDs) were analyzed for immersion dose. Particulate filters, air iodine cartridges, precipitation, vegetation, soil, and crops were analyzed for atmospheric radiation and fallout. Well water, surface water, aquatic sediment, and clams, as well as the aforementioned media, were analyzed because of their close association with either plant effluents and/or man's consumption. All results from these analyses are reported in Tables 15 through 18.

Film badges used during the reporting period were inadvertently exposed to gamma radiation in transit. As a result, the high levels of exposure are not representative of environmental radiation levels and in no way represent environmental impact of OCNGS operation.

Thermoluminescent dosimeters reflect environmental exposures. 1

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

Sampling Techniques This sampling process is conducted around the OCNGS as described below:

Environmental Media / Pathway Mode of Sampling Atmosphere / direct radiation, Composite of Air Particulates inhalation on filter Adsorption of air iodines on charcoal filter Atmosphere / direct radiation TLD/ Film Badge Surface Water / ingestion Grab Sample Well Water / ingestion Grab Sample Precipitation / direct radiation Composite Vegetation, Crops / ingestion Grab Soil / direct radiation Grab Aquatic Sediment / direct radiation Grab Shellfish / ingestion Grab All samples collected are processed and packed at an offsite lab near the OCNGS, then shipped to the vendor laboratories by overland courier for analysis. Vendor laboratories prepare samples as instructed by the Oyster Creek Environmental Controls Department.

Radiochemical analyses are then performed by vendor laboratory, and results are sent to the Oyster Creek Environmental Controls Department.

- i

~

Data Tables 15 through 20 represent a summary of all radiological environmental data for the reporting period. Tables 18, 19, and 20 present the data in the manner prescribed in proposed USNRC Regulatory Guide 4.8 and USNRC Branch Technical Position.

I t

a 4

m I. -..

TABLE 14 OYSTER CREEK STATION ENVIRONMENTAL MONITORING STATIONS LOCATION AND SAMPLE TYPE COLLECTED STATION NUMBER SAMPLE COLLECTED 1

Forked River, N.J. - Oyster Creek APT, AIO, RG, RWA, Meteorological Tower VGTN, SOIL, WWA Tl Forked River, N.J. - Oyster Creek RG Meteorological Tower 2

Pinewald, N.J. - Route 99 at JCP&L APT, AIO, RG, RWA, Company Pinewald Substation north VGTN, SOIL of Forked River, N.J.

3 Island Beach State Park, N.J. -

APT, AIO, RG, RWA, Near old Coast Guard Station VGTN, SOIL 4

Barnegat, N. J. - Route 1534, APT, AIO, RG, RWA, Windward at Barnegat, first VGTN, SOIL coad West of Parkway Exit 5

Forked River, N.J. - Garden APT, AIO, RG, RWA, State Parkway Northbound Entrance VGTN, SOIL to Holiday House 6

Forked River, N.J. - Lane Place RG behind St. Pius X Catholic Churc'h 7

Waretown, N.J. - Compass Road, RG second pole North of Bay Parkway 8

Waretown, N.J. - Route 99 at the RG Waretown Substation 9

Waretown, N.J. - Route #532, North RG side of road at Parkway 10 Toms River, N.J. - Route $37 East, RG adjacent to " Eastern Off Road Supply" 11 Harvey Cedars, N.J. - Long Beach RG Blvd. and East 70th Street, Long Beach Island 12 Cedar Run, N.J. - Route 89, East of RG Assembly of God Church !

J

TABLE 14 OYSTER CREEK STATION ENVIRONMENTAL MONITORING STATIONS LOCATION AND SAMPLE TYPE COLLECTED S_TATION NUMBER SAMPLE COLLECTED 13 South Toms River, N.J. - Dover Road, RG next to last pole traveling West on North side 14 Lakewood, N.J. - Larrabee Substation, RG just off Route 4547 on Randolph Road 15 New Egypt, N.J. - Route #539, last RG pole on South side, adjacent to "Bomarc" Site 16 Intersection of Route #563 and RG Route 472, two poles South 17 New Gretns, N.J. - Route #563, RG 2 miles North, next to High Voltage Line le Forked River, N.J. - Lacey Road, WWA Townsend's Marina 19 Forked Riyer, N.J. - 1015 Inland WWA Road, Forked River Beach 20 Forked River, N.J. - Finninger Farm WWA at Environmental Lab 21 Waretown, N.J. - 215 Dock Avenue, WWA Sands Point Harbor 22 Waretown, N.J. - 1014 Long John, WWA Silver Way, Skippers Cove 23 Barnegat Bay - Off Stouts Creek SWA, AQS, CLAM approximately 400 yards SE (150*)

of FL "1" (Heading on BWN "D")

24 Barnegat Bay - Approximately SWA, AQS, CLAM 250 yards SE (180') of FL "3" (Heading on N "66")

i.

n

TABLE 14 OYSTER CREEK STATION ENVIRONMENTAL MONITORING STATIONS LOCATION AND SAMPLE TYPE COLLECTED STATION NUMBER SAMPLE COLLECTED 25 Barnegat Bay - Off Holiday Harbor; SWA, AQS, CLAM approximately 200 yards SE (140*)of the Lagoon Mouth 26 Forked River, N.J. - South Branch SWA,'AQS of Forked River, North of Bridge to Visitor Center 27 Forked River, N.J. - Downstream SWA, AQS of Oyster Creek Fire Pcod, approximately 10 yards 28 Forked River, N.J. - Lacey Road CROP and the Garden State Parkway 29 Forked River, N.J. - Route #534 CROP and the Garden State Parkway 30 Forked River, N.J. - Finninger Farm CROP along fence 31 Manahawkin Bay - Approximately 25 SWA, AQS, CLAM yards SE (140') of C "23" and N "24" 32 Oyster Creek - Mouth of Creek midway SWA, AQS between Bulkhead on North Shore and South Shore of Creek 33 Oyster Creek - Approximately 1200 SWA, AQS yards East of Route #9 Bridge, in middle of channel, directly South of Bulkhead running perpendicular to North Shore A

Allenhurst, N.J. - JCP&L Company APT, AIO, RG, RWA District Headquarters C

Cookstown, N.J. - Route #528 Spur, APT, AIO, RG, RWA at JCP&L Company District Dispatcher -

TABLE 14 OYSTER CREEK STATION ENVIRONMENTAL MONITORING STATIONS LOCATION AND SAMPLE TYPE COLLECTED STATION NUMBER SAMPLE COLLECTED H

Hammonton, N.J. - Egg Harbor Road, APT, AIO, RG, RWA at the Atlantic City Electric District Dispatcher APT = Air Particulate AIO = Air Iodine RG

= Radiogas/ Direct Radiation RWA = Precipitation WWA = Well Water SWA = Surface Water AQS = Aquatic Sediment CLAM = Clams CROP = Pasture / Crops VGTN = Vegetation SOIL = Soil f

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GAMMA DOSE TO THE ENVIRDNMENT (MR)

_____________________.m AS MEASURED BY THERMOLUMINESCEH1 DOSIMEICR FCR JUNE,1982 THROU0ii NOVEMBER,lo.32 (MONTHLY TLD READINGS)

ANALYSIS DATE:

07JUL82 02AUG82 30AUG82 24SEP82 220CT82 22HOV82 COLLECT DOSE COLLECT DOSE COLLECT 00SE 3-M0 COLLECT L!OSE COLLFCT DDSE COLLECT DDSE 3-MO 6-MO STATI0H DATE DATE DATE TOTAL DATE DATF DATE TOTAL TOTAL A 23JUH82 6.27 21JUL82 4.52 18AUG82 6.11 16.90 15SEP8?

5.53 12GCT82 6.97 10HOV82 5.84 18.34 35.24 C 22JUH82 5.57 20JUL82 4.36 17AUG82 5.71 15.64 175EP82 4.47 140CT82 5.97 09HOV82 4.97 15.41 31.05 H 22JUH82 5.11 20JUL82 3.37 17AUG82 4.99 13.47 175EP82 4.51 140CT32 5.24 09HOV82 3.98 13.73 27.20 1 24JUH82 6.65 19JUL82 4.66 16AUG82 6.90 18.21 14SEP82 5.50 130Cr82 6.92 IlHOV82 5.00 17.42 35.63 2 24JUH82 4.72 23JUL82 2.73 20AUG82 4.90 12.35 20SEP82 4.49 160CT82 6.90 llHOV82 4.10 15.49 27.84 3 24JUH82 4.92 21JUL82 2.79 18AUG82 4.66 12.37 165EP32 4.80 180c182 5.72 10HOV82 4.91 15.43 27.80 4 25JUH82 4.30 22JUL82 2.89 20AUG82 4.98 12.17 20SEP 2 4.28 160CT82 5.91 09HOV82 3.99 14.18 26.35 5 23JUH82 4.14 23JUL82 3.11 20AUG82 5.07 12.32 15SEP82 5.15 160CT82 5.72 10H0V82 4.34 15.21 27.53 6 23JUH82 5.30 21JUL82 3.00 18AUG82 5.06 13.36 14SEP82 4.26 160CT82 4.92 llHOV82 4.37 13.55 26.91 7 22JUH82 4.75 23JUL82 2.52 23AUG82 5.09 12.36 21SEP82 4.21 160CT82 5.30 15HOV82 4.3V 13.90 26.26 8 22JUH82 4.70 23JUL82 2.62 19AUG82 5.16 12.48 16SEP82 4.10 160Cf82 5.26 12HOV82 3.72 13.08 25.56 9 22JUH82 5.62 22JUL82 3.12 19AUG82 5.53 14.27 17SEP32 5.09 1600T82 6.13 15HOV82 4.98 16.20 30.47 Tl 24JUH82 6.62 19JUL82 4.74 16AUG82 6.23 17.59 14SEPS2 5.16'130CT82 6.63 IINOV82 5.45 17.24 34.83 10 23JUH82 4.35 23JUL82 2.84 20AUG82 5.51 12.70 16SEP82 4.23 160CT82 5.53 10HOV82 4.29 14.05 26.75 11 25JUH82 4.54 22JUL82 2.58 19AUG82 4.85 11.97 20SEP82 4.41 180CT82 5.53 12HOV82 3.96 13.90 25.87 12 22JUH82 4.32 20JUL82 2.75 19AUG82 5.17 12.24 17SEP82 4.20 160CT82 5.53 09HOV82 4.39 14.12 26.36 13 23JUH82 4.79 23JUL82 2.73 20AUG82 5.17 12.69 16SEP82 3.98 160CT82 5.45 10HOV82 4.07 13.50 26.19 14 23JUH82 6.05 21JUL82 3.76 18AUG82 6.14 15.95 15SEP82 5.52 17UCT82 6.53 10HOV82 5.48 17.53 33.48 15 22JUH82 4.82 20JUL82 2.69 17AUG82 4.59 12.10 17SEP82 3.85 140CT82 5.64 09HOV82 3.99 13.48 25.58 16 25JUN82 4.08 22JUL82 3.55 19AUG82 4.88 12.51 175EP82 3.79 180CT82 5.12 12HOV82 4.39 13.30 25.81 17 22JUH82 5.18 20JUL82 3.15 17AUG82 5.28 13.61 175EP82 4.25 140CT82 6.19 09HOV82 4.44 14.88 28.49 eng -~

4 TABLE 17 RADIOLOGICAL ENVIRONMENTAL N0HITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE.1982 THROUGH NOVEMBER,1982 THE FOLLOWING PAGES ARE A

SUMMARY

OF REMP DATA FOR 1HE SCHEDULED COLLECTION PERIOD JUNE.1982 THRU HOVEMBER,I982. DATA IS SUMMARIZED ON A SEMI-AHHUAL AND QUARTERLY BASIS, WHERE I.) XXX-MEAH(H/ TOTAL); MEAN AND RANGE BASED OH RANGE DETECTABLE ACTIVITIES OF ALL XXX STATIONS 2.) XXX: BACKGROUND OR INDICATOR STAIIOris 3.) (H/TCTAL): FRACTION OF DETECTABLs ACTIVITTES/

TOTAL HUMBER OF AHALYSES PERFORMED 4.) STATIOH: Sir >

WITH HIGHEST SEMI-AHhUAL MF4H 5.) BACKGROUN'i aiIGHS USED ARE:

STATION A,C,H 31 SAMPLE TYPE AIR PARTICULATE SchlMEHf AIR IODIHE CLAMS PRECIPITATION SU3 FACE WATER

.6.) IN ADDITIDH,THE FOLLOWING FOOD PRODUCTS WERE SAMP3.ED FOR GAMMA ISOTOPIC CONTENT DURING Tl?E SUMf1ER MUHil8St SAMPLE TYPE STATJOH CORN 1,2,3,4,0 CABBAGE I,C TOMATOES 2,3,4,5,A,H CUCUMBERS 5

GREEN BEANS A.H

TABLE 18 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE 1982 THROUGil NOVEMBER,1982 SEMI-AHNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED j

OF RANGE RANGE FOR INDICATOR MEAtt ANALYSES PERFORMED STATIDH STATIDH-MEAH(H/ TOTAL)

RANGE VEGETATIDH GROSS BETA 30 3.31E+01 2.29E+03 (30 /30 )

(.

/, )

I 2 3 4 5 (PCI/KG(WET))

( 1.48E+03 - 3.89E*03)

(

)

2 2.80E+03(6 /6 )

t

( 2.46E+03 - 3.89E+03)

AIR PARTICULATE GROSS ALPHA 103 6.03E-04 1.44E-03 (46 /65 )

1.31E-03(30 /38 )

1 2 3 4 5 (PCI/M3

)

( 5.22E 3.64E-03)

( 3.32E 2.43E-03) 5 1.62E-03(11 /13 )

( 9.06E 3.64E-03)

AIR PARTICULATE GROSS BETA 103 5.38E-03 1.60E-02 (56 /65 )

. 1.54E-02(37 /38 )

1 2 3 4 5 (PCI/M3

)

( 7.32E 2.97E-92)

( 3.59E 2.81E-02) 5 1.83E-02(12 /13 )

( 1.04E 2.97E-02)

AIR PARTICULATE GELI GAMMA CE-144 102 3.40E-02

< LLD (0 /64 )

< LLD (0 /38 )

1 2 3 4 5 (PCI/M3

)

< LLD (0 /13 )

AIR PARTICULATE GELI GAMMA AG-110M 103 5.28E-03

< LLD (3 /65 )

< LLD (0 /38 )

1 2 3 4 5 (PCI/M3

)

/

5

< LLD (0 /13 )

~~ AIR PARTICULATE GELI GAMMA SR-91 1

3.80E-05

< LLD (0 /1 )

(.

/. )

3 (PCI/M3

)

(

)

3

< LLD (0 /1 )

AIR PARTICULATE GELI GAMMA TE-129M 103 2.38E-01

< LLD (0 /65 )

< LLD (0 /38 )

1 2 3 4 5 l

(PCI/M3

)

5

< LLD (0 /13 )

O i

I

RADIOLOGICAL EHVIRONMENTAL MONITOR 194 PROGRAM

SUMMARY

OYSTER CREEK NUCLEAR CFHERATING STATION JUNE.1982 THROHGil HUVEMBER,1982 SEMI-AHHUAL SUMttAR~t SANPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR PEAHth/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR IllDICAIOR MEAN ANALYSES PERFORMED

$7ATIDH SlATIOH-MEAH(H/ TOTAL) 9ANGE AIR PARTICULATE GELI GAMMA MO-99 83 4.02E-01

< LLD (0 /54 )

< LLD (0 /29 )

1 2 3 4 5 (PCI/M3

)

5

< LLD (0 /9 )

AIR PARTICULATE GELI GAMMA 2RHB-95 55 6.32E-03

< LLD (0 /35 )

< LLD (0 /20 )

1 2 3 4 5 (PCI/M3

)

5 LLD (0 /7 )

AIR PARTICULATE GELI GAMMA CS-134 103 4.91E-03

< LLD (G /65 )

< LLD (0 /38 )

1 2 3 4 5 (PCI/M3

)

5

< LLD (0 /13 )

AIR PARTICULATE GELI GAMMA CD-58 103 6.08E-03

< LLD (0 /65 )

< LLD (O /38 )

1 2 3 4 5 (PCI/M3

)

5

< LLD (0 /13 )

AIR PARTICULATE GELI GAMMA MH-54 103 5.53E-03

< LLD (G /65 )

< LLD (0 /38 )

1 2 3 4 5 (PCI/M3

)

5

< LLD (0 /13 )

AIR PARTICULATE GELI GAMMA TH-232 103 1.86E-02

< LLD (0 /65 )

< LLD (0 /38 )

1 2 3 4 5 (PCI/M3

)

5

< LtD (0 /13 )

AIR PARTICULATE GELI GAMMA FE-59 103 1.34E-02

< LLD (O'/65 )

< LLD (0 /38 )

1 2 3 4 5 (PCI/M3

)

5

< llD (0 /13 )

$ I

~

RADIOLOGICAL ENVIRONMEH1TL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GEHERATIrlu STATICH JUNE.1982 THROUGH HOVEMBER,1982 SEMI-ANNUAL SUMMARf SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(M/10iAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RAHGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATIDH STATI0H-MEAH(H/ TOTAL)

RANGE AIR PARTICULATE GELI GAMMA CS-136 103 1.41E-02

< ILD (0 /65 )

< LLD (0 /38 )

1 2 3 4 5 (PCI/M3

)

5

< LLD (0 /13 )

AIR PARTICULATE GELI GAMMA ZH-65 103 1.24E-02

< LLD (0 /65 )

< LLD (0 /38 )

1 2 3 4 5 (PCI/M3

)

< LLD (0 /13 )

/

AIR PARTICULATE GELI GAMMA CD-60 103 7.55E-03

< LLD (0 /65 )

< LLD (O /38 )

1 2 3 4 5 (PCI/M3

)

5

< LLD (0 /13 )

AIR PARTICULATE GELI GAMMA K-40 103 9.10E-02 3.58E-01 (2 /65 )

1.94E-01(3 /38 )

1 2 3 4 5 (PCI/M3

)

( 7.70E 6.40E 01)

( 8.30E 3.80E-01) 5 3.58E-01(2 /13 )

( 7.70E 6.40E-01)

AIR PARTICULATE GELI GAMMA BALA-140 103 1.85E-02

< LLD (0./65 )

< LLD (0 /38 )

1 2 3 4 5 (PCI/M3

)

5

< LLD (0 /13 )

AIR PARTICULATE GELI GAMMA BE-7 103 6.59E-02 1.01E-01 (25 /65 )

8.00E-02(17 /38 )

1 2 3 4 5

~~

(PCI/M3

)

( 6.10E 1.50E-01)

( 2.80E 1.50E-01) 4 1.40E-01(2 /13 )

( 1.30E 1.50E-01)

AIR PARTICULATE GELI GAMMA ZR-95 48 1.09E-02

< LLD (0 /30 )

< LLD (O /18 )

1 2 3 4 5 (PCI/M3

)

5

< LLD (0 /6 ) l

s.

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM $UMMARY OYSTER CREEK HUCLEAR GF.HERATING STATION JUNE,1982 THRDUGH NOVEMBER 1982 SEMI-AHHUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOT0FE HUMBER LLD INDICATOR-MEAM(H/iOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAH ANALYSES PERFORMED STATION STATIDH-MEAH(H/ TOTAL)

RANGE i

AIR PARTICULATE GELI GAMMA HB-95 48 7.42E-03

< LLD (9 /30 )

< LLD (0 /18 )

1 2 3 4 5 (PCI/M3

)

5

< LLD (0 /6 )

AIR PARTICULATE GELI GAMMA

$8-125 103 1.48E-02

< LLD (0 /65 )

< LLD (0 /38 )

1 2 3 4 5 (PCI/M3

)

5

< LLD (0 /13 )

AIR PARTICULATE GELI GAMMA CE-141 102 1.15E-02

< LLD (0 /64 )

< LLD (0 /38 )

1 2 3 4 5 (PCI/M3

)

1 5

< LLD (0 /13 )

AIR PARTICULATE GELI GAMMA RU-103 103 6.99E-03

< LLD (0 /65 )

< LLD (0 /38 )

1 2 3 4 5 (PCI/M3

)

5

< LLD (0 /13 )

AIR PARTICULATE GELI GAMMA CR-51 103 6.73E-02

< LLD (0 /65 )

< LLD (0 /38 )

1 2 3 4 5 (PCI/M3

)

5

< LLD (0 /13 )

AIR PARTICULATE GELI GAMMA RA-226 103 1.63E-02

< LLD (0 /65 )

< LLD (O /38 )

1 2 3 4 5 (PCI/M3

)

< LLD (0 /13 )

AIR PARTICULATE GELI GAMMA I-131 102 2.82E-02

< LLD (0 /64 )

< LLD (0 /38 )

1 2 3 4 5 (PCI/M3

)

5

< LLD (0 /13 )

-- e

~

RADIOLOGICAL EHVIRONMENTAL MOHITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATINC STATICH JUNE.1982 THROUGH NOVEMSER.1932 SEMI-AHHUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MCAH(h' TOTAL)

BACKROUND-MEAH(N/ TOTAL)

STATI0HS USED OF RANGE RANGE FOR INDICATOR MEAH ANALYSES PERFORMED STATI0ti STATI0H-MEAH(H/ TOTAL)

RANGE AIR PARTICULATE GELI GAMMA HP-239 41 5.96E+01

< LLD (0 '26 )

< LLD (0 /15 )

1 2 3 4 5 (PCI/M3

)

5

< LLD (0 /3 )

AIR PARTICULATE GELI GAMMA RU-106 103 4.72E-02

< LLD (0 /(5 3

< LLD (0 /38 )

1 2 3 4 5 (PCI/M3

)

5

< LLD (0 /13 )

AIR PARTICULATE GELI GAMMA CO-57 96 4.17E-03

< LLD (9 /60 )

< LLD (0 /36 )

1 2 3 4 5 (PCI/M3

)

5

< L L D ( 0 /12 )

AIR PARTICULATE GELI GAMMA I-133 1

4.30E-04

< LLD (0 /1 )

(,

/. )

3 (PCI/M3

)

(

)

3

< ILD (0 /1 )

AIR PARTICULATE GELI GAMMA CS-137 103 5.51E-03

< LLD (0 /65 )

< LLD (0 /38 )

1 2 3 4 5 (PCI/M3

)

5

< LLD (0 /13 )

AIR PARTICULATE STRONTIUM-89 8

8.55E-04 6.01E-04 (1 /5 )

2.32E-04(1 /3 )

1 2 3 4 5 (PCI/M3

)

( 6.01E 5.01E-04)

( 2.32E 2.32E-04) 3 6.01E-04(1 /1 )

( 6.01E 6.01E-04)

AIR PARTICULATE STRONTIUM-90 8

7.06E-04

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/M3

)

~2 5

< LLD (0 /1 ) I

RADIOLOGICAL ENVIRONMENTAL MOHITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STA110H JUNE.1982 THROUGH HOVEt1BER,1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUM 0ER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED 0F RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STAi!OH STA1IDH-MEAH(H/ TOTAL)

RANGE i

PRECIPITATIDH GROSS BETA-SS 48 1.59E+00-5.41E400 (3 /30 3 1.07E+00(2 /18 )

1 2 3 4 5 (PCI/L

)

( 4.055 1.45E601)

( 9.73E 1.16E+00) 2 1.45E+01(1 /6 )

( 1.45E401 - 1.45E+01) t PRECIPITATION GROSS BETA-DS 48 1.61E+00 4.31E+00 (23 /30 )

3.66E+00(15 /18 )

1 2 3 4 5 (PCI/L

);

( 9.95E 9.76E+00)

( 1.45E+00 - 7.43E+00) 2 5.25E+00(6 /6 )

( 2.49E+00 - 9.76E+00)

PRECIPITATIDH GELI GAMMA CE-144 8

8.34E+01

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /1 )

PRECIPITATION GELI GAMMA AG-110M 8

9.15E+00

< LLD (0 /5 )

< LLD (0 /3 3 1 2 3 4 5 (PCI/L

)

5

< LLD (0 /1 )

i PRECIPITATION GELI GAMMA TE-129M 8

3.96E*02'

< LLD (0 /9 1

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

3

< LLD (0 /1 )

"~ RECIPITATIDH GELI GAMMA MD-99 8

5.24E+02

< LLD (C /5 )

< LLD (0 /3 )

1 2 3 4 5 P

(PCI/L

)

5

< L(D (0 /1 )

PRECIPITATION GELI GAMMA CS-134 8

8.72E+00

< LLD (0 /5 )

< LLD (0/33 1 2 3 4 5

,_ (PCI/L

)

5

< LLD (0 /1 ).

1

m RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERAT!NG STATION JUNE.1982 THROUGH NOVEMhER,1982 SEMI-AHHUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MFAH(0/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICAIOR MEAH ANALYSES PERFORMED STATIDH STATION-MEAH(H/ TOTAL)

RANGE PRECIPITATION GELI GAMMA CD-58 8

9.89E+00

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

a 5

< LLD (0 /1 )

PRECIPITATION GELI GAMMA MH-54 8

8.76E+00

< LLD (0 /5 )

< LLD (0 /3 )

I 2 3 4 5 (PCI/L

)

5

< LLD (0 /1 )

PRECIPITATIDH GELI GAMMA TH-232 8

2.99E+01

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /1 )

PRECIPITATION GELI GAMMA FE-59 8

1.85E+01

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /1 )

PRECIPITATION GELI GAMMA CS-136 8

1.89E+01

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /1 )

PRECIPITATIDH GELI GAMMA ZH-65 8

1.69E+01

< LLD, (0 /5 )

< LLD (0 /3 )

1 2 3 4 5

__ (PCI/L

)

5

< LLD (O /1 )

PRECIPITATION GELI GAMMA CD-60 8

7.89E+00

< LLD (0 /5 )

< LLD (0 /3 )

1. 2 3 4 5 (PCI/L

)

l 5

< LLD (0 /1 )

w RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GEHERA11H; STATION JUNE.1982 THROUGH NOVEMBER,1982 SEMI-AHHUAL

SUMMARY

SAMPLE TYPE AHALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(N/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAH ANALYSES PERFORMED STATION SIAT10H-MEANCH/ TOTAL)

RANGE PRECIPITATION GELI GAMMA K-40 8

6.90E+01

< LLD to /5 )

< LtD (0 /3 )

1 2 3 4 5 (PCI/L

)

< E L D ( 0 /1 )

PRECIPITATIDH GELI GAMMA BALA-140 8 1.67E+01

< LLD (0 #5 }

< I LD (0 /3 )

1 2 3 4 5 (PCI/L

)

3

< LLL (0 /1 )

PRECIPITATIDH GELI GAMMA BE-7 8

9.92E+01

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

5

< I LD (0 /1 )

PRECIPITATION GELI GAMMA ZR-95 8

1.85E+01

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

5

< LLC (0 /1 )

PRECIPITATIDH GELI GAMMA HB-95 8

1.17E+01

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /1 )

PRECIPITATIDH GELI GAMMA SB-125 8

2.91E+01

< LLD (0 /5 i

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /1 )

PRECIPITATION GELI GAMMA CE-141 8

2.41E+01

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /1 )

-~._

RADIOLOGICAL ENVIRONMENTAL MOHITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH JUNE.1982 THROUGil NOVEMRER.193?

SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAN(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATION STATIDH-MEAH(H/ TOTAL)

RANGE l

t PRECIPITATION GELI GAMMA RU-103 8

1.25E+01

< LLD (0/51

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /1 )

PRECIPITATION GELI GAMMA CR-51 8

1.22E+02

< LLD (0 /5 ?

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

i 5

< LLD (0 /1 )

PRECIPITATIDH GELI GAMMA RA-226 8

1.82Et01

< LLD (0 /5 1

< LLD (O /3 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /1 )

PRECIPITATION GELI GAMMA I-131 8

3.81E+01

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /1 )

PRECIPITATION GELI GAMMA HP-239 6

1.67E+05

< LLD (0 #5 )

< LLD (0 /1 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /1 )

PRECIPITATION GELI GAMMA RU-106 8

9.02E+01

< LLD (o /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /1 )

PRECIPITATION GELI GAMMA CO-57 8

1.09E+01

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0- /1 )

~

k '

l

RADIOLOGICAL ENVIRONMENTAL MGRIIDR!HQ PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GFHERATING STATIGH JUNE.1982 THROUGH HOVEM;EE.1982 SEMI-ANNUAL SUFMARY SAMPLE TYPE ANALYSIS ISDTOPE HUMBER LLD INDICATOR-siEAH(H/T0iAL)

BACKROUND-MEAH(H/ TOTAL)

STATI0HS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATION STATIDH-MFANCH/ TOTAL)

RANGE t

PRECIPITATIDH GELI GAMMA CS-137 8

9.37E*00

< LLD (6/51

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /1 )

PRECIPITATION TRITIUM 48 1.51E+02 2.65F402 (2 /30 ?

4.31E+02(1 /18 )

1 2 3 4 5 (PCI/L

)

( 1.88E+02 - 3.42Et02)

( 4.81E+02 - 4.81E+02) 2 3.42E602(1 /6 )

( 3.42E+02 - 3.42E+02)

PRECIPITATION HAI GAMMA CE-144 40 7.91E+01

< LLD (0 /25 )

< LLD (0 /15 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /5 )

PRECIPITATION HAI GAMMA AG-110M 40 6.77E+00

< LLD (0 /25 )

< LLD (0 /15 )

1 2 3 4 5 (PCI/L

)

5 C LLD (0 /5 )

PRECIPITATION HAI GAMMA TE-129M 40 1.41E+02

< LLD (0 /25 )

< LLD (O /15 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /5 )

PRECIPITATIDH HAI GAMMA MD-99 40 2.62E+03

< LLD (0 /25 )

< LLD (0 /15 )

1 2 3 4 5 (PCI/L

)

5

< LLD (O /5 )

PRECIPITATION HAI GAMMA ZRHB-95 40 7.11E+00

< LLD (0 /25 )

< LLD (0 /15 )

1 2 3 4 5 (PCI/L

)

~~

5

< LLD (0 /5 ) i

1 RADIOLOGICAL ENVIR0tlMENTAL MONITORING l'ROCPAM dUMMARY OYSTER CREEK NUCLEAR GENERATIN3 STATIUM JUNE,1982 THROUGH NMEMBER.1987 SEMI-ANNUAL SUMr*4RY SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDI*7 Ai oR-MCAH(N/10T AL )

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES

~

PERFORMED STATION STATIDH-MEAH(H/ TOTAL)

RANGE PRECIPITATIDH HAI GAMMA CS-134 40 6.49E+00

< LLD (0 /25 )

< LLD (0 /15 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /5 )

PRECIPITATION HAI GAMMA CO-58 40 7.29E+00

< ILD (0 /25 )

< LLD

( 0 /15 )

1 2 3 4 5 (PCI/L

)

e 5

< LLD (0 /5 )

PRECIPITATIDH HAI GAMMA MH-54 40 6.53E+00

< LLD to #25 )

< LLD (0 /15 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /5 )

PRECIPITATIDH HAI GAMMA TH-232 40 2.51E+01

< LLD (0 /25 )

< LLD (0 /15 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /5 )

PRECIPITATION HAI GAMMA FE-59 40 1.48E+01

< LLD (0 /25 )

< LLD (0 /15 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /5 )

PRECIPITATION HAI GAMMA CS-136 40 1.97E+01

< LLD (0 /25 )

< LLD (0 /15 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /5 )

PRECIPITATION HAI GAMMA TE-132 40 2.58E+02

< LLD (O /25 )

< LLD (0 /15 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /5 )

l I

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK NUCLEAR GENERATING STATION JUNE.1982 THROUGH NOVEMBER ls32 SEMI-AHHUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATIDH STATIDH-MEAH(H/ TOTAL)

RANGE PRECIPITATION HAI GAMMA ZH-65 40 1.39E+01

< LLD (O./25 )

< LLD (0 /15 )

1 2 3 4 5 (PCI/L 3

5

< LLD (0 /5 )

PRECIPITATION HAI GAMMA CD-60 40 6.86E+00

< LLD (0 /25 )

< LLD (0 /15 3.

I 2 3 4 5 (PCI/L

)

5

< LLD (0 /5 )

PRECIPITATION HAI GANMA K-40 40 7.80E+01

< LLD (0 /25 3

< LLD (0 /15 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /5 )

PRECIPITATION NAI GAMMA BALA-140 40 1.55E+01

< LLD (0 /25 )

< LLD (0 /15 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /5 )

PRECIPITATION HAI GAMMA BE-7 40 7.70E+01

< LLD (O /25 )

< LLD (0 /15 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /5 )

PRECIPITATIDH HAI GAMMA CR-51 40 9.23E+01

< LLD (0 /25 )

< LLD (0 /15 )

1 2 3 4 5

__ (PCI/L

)

5

< LLC (P /5 )

PRECIPITATION HAI GAMMA RA-226 40 1.25E+01

< LLD (0 /25 )

< LLD

( 0 /15 )

1 2 3 4 5 (PCI/L

)

< LLD (0 /5 )

~ _

RADIOLOGICAL ENVIRONMENTAL MOHITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GE!!ERATINu STATIDH JUNE.1982 THROUGH NOVEMBER.1982 SEMI-AHHUAL SUMMARV SAMPLE TYPE AHALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAN(tarTOTAL)

BACXROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATION STATIDH-MEAH(H/ TOTAL)

RA!!GE

.a PRECIPITATIDH HAI GAMMA I-131 40 2.89E+01

< LLD (0 /2.5 )

< LLD (0 /15 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /5 )

PRECIPITATION HAI GAMMA HA-22 40 6.76E+00

< LLD (0 /25 )

< LLD (0 /15 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /5 )

PRECIPITATIDH HAI GAMMA RU-106 40 6.57E+01

< LLD (0 /25 )

< LLD (0 /15 3 1 2 3 4 5 (PCI/L

)

5

< LLD (0 /5 )

PRECIPITATIDH HAI GAMMA I-133 40 7.68E+00

< LLD (O /25 )

< LLD (0 /15 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /5 )

PRECIPITATIDH HAI GAMMA CS-137 40 7.22E+00

< LLD (0 /25 3

< LLD (0 /15 )

1 2 3 4 5 (PCI/L

)

5

< LLD (0 /5 )

PRECIPITATION STRONTIUM-89 48 1.10E+00 6.40E-n1 (1 /30 )

< LLD (0 /18 )

1 2 3 4 5 (PCI/L

)

( 6.40E 6.40E-01) 2 6.40E-01(1 /6 )

( 6.40E 6.40E-01)

PRECIPITATION STRONTIUM-90 48 9.64E-01

< LLD (O /30 )

< LLD (0 /18 )

1 2 3 4 5 (PCI/L

)

~~

5

< LLD (O /6 ),

RADIOLOGICAL ENVIRONMENTAL M0HITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH JUNE.1982 THROUGil H0VEMBER.1982 SEMI-AHHUAL

SUMMARY

3 AMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATIDH STAT 10H-MEAH(H/ TOTAL)

RAHOE AIR IODINE IODINE-131 102 2.71E-02

< LLD (0 /6S )

< LLD (0 /37 )

1 2 3 4 5 (PCI/M3

)

5

< I LD (9./13 )

CABBAGE HAI GAMMA CE-144 2

4.85E+01

< LLD (0 /1 )

1 (PCI/KG(WET))

1

< LLL (0 /1 )

i CABBAGE HAI GAMMA AG-110M 2

1.20E+01

< LLD (0 /1 7

< LLD (0 /1 )

1 (PCI/KG(WET))

1

< LLD (0 /1 )

i CABBAGE HAI GAMMA TE-129M 2

2.20E+02

< LLD

( 0 /1 J

< LLD

( 0 /1 )

1 (PCI/KG(WET))

1

< LLD (0 /1 )

l CABBAGE HAI GAMMA MD-99 2

5.35E+03

< LLD to /1 )

< I LD (0 /1 )

1 (PCI/KG(WET))

1

< Lib (0 /1 )

~

i 4

CABBAGE HAI GAMMA ZRHB-95 2

1.40E+01

< LLD (0 /1 )

< LLC (0/11 1

l (PCI/KG(WET))

l 1

< LtD (0 /1 )

CABBAGE HAI GAMMA CS-134 2

1.25E+01

< LLD (0 /1 )

1 (PCI/KG(WET))

1

< LLD (0 /1 )

E

},

i

RADIDLOGICAL ENVIRONMENT AL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STAT 10H JUNE.1982 T!I400GH HOVENBER,1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE AHALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICAIOR MEAN

.AHALYSES PERFORMED STATION STATIDH-NEAH(H/ TOTAL)

RANGE CABBAGE HAI GAMeiA CO-58 2

1.35E+01

< LLD (0 /1 )

1 (PCI/KG(WET))

1

< LLD (C /1 )

CABBAGE HAI GAMMA MH-54 2

1.30E+01

< LLD (0 /1 )

< LLD

( 0 /1 )

1 (PCI/KG(WET))

1

< LLO (0 /1 )

CABBAGE HAI GAMMA TH-232 2

4.70E+01

< LLD (0 /1 )

1 (PCI/KG(WET))

1

< LLD (0 /1 )

CABBAGE HAI GAMMA FE-59 2

3.00E+01

< LLD

( 0 /1' )

< LLD (0 /1 )

1 (PCI/KG(WET))

1

< LLD (0 /1 )

CABBAGE HAI GAMMA CS-136 2

3.65E+01

< LLD

( 0 /1 1

< LLD

( 0 /1 )

1 (PCI/KG(WET))

1

< I LD (0 /1 )

CABBAGE HAI GANMA TE-132 2

2.55E+02

< LLD (0 /1 )

< LLD

( 0 /1 3 1

__ (PCI/KGCWET))

1

< LLD (0 /1 )

1

,a CABBAGE HAI GAMMA ZH-65 2

3.-25E+01

< LLD (0 /1 )

< LLD (0 /1 3 1

(PCI/KG(WET))

r 1

< LLD (0 /1 )

- l

c RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK NUCLEAR GENERATING STATION JUNE.1982 THROUGH HOVEMBER,1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAN(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATION STATION-MEAH(H/ TOTAL)

RANGE CABBAGE HAI GAMMA CO-60 2

1.25E+01

< LLD (0 /1 1

< LLD

( 0 /1 )

1 (PCI/KG(WET))

1

< LLD (0 /) )

CABBAGE HAI GAMMA K-40 2

3.10E+02 1.80E+03 (1 /1 )

2.50E+03(1 /1 )

1 (PCI/KG(WET))

( 1.80E+03 - 1.80E103)

( ?.59E+03 - 2.50E+03) i

~

l 1.30E+03(1 /1 )

( 1.80E+03 - 1.80E*03)

CABBAGE HAI GAMMA BALA-140 2 2.85E+01

< LLD (0 /1 )

1 (PCI/KG(WET))

I

< LLD (0 /1 )

CABBAGE HAI GAMMA BE-7 2

1.15E+02

< LLD (0 /1 )

'l (PCI/KG(WET))

1

< LLD (0 /1 )

CABBAGE HAI GAMMA CR-51 2

1.15E+02

< LLD (0 /1 )

1 (PCI/KG(WET))

1

< LLD (0 /1 )

"" CABBAGE HAI GAMMA RA-226 2

2.35E+01

< LLD (O /1 )

< LLD

( 0 /1 )

1 (PCI/KG(WET))

1

< LLD (0 /1 )

CABBAGE HAI GAMMA I-131 2

4.10E+01

< LLD (0 /1 )

1 (PCI/KG(WET))

"2 1

< LLD (0 /1 )

. I

i RADIOLOGICAL ENVIRONMENTAL MONITORIHG PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING sTATICH JUNE.1982 THROUGH NOVEMBER,1982 SEMI-ANNUAL

SUMMARY

9 AMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD -INDICATOR-MEAN(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAH ANALYSES PERFORMED STATIDH STATIDH-MEAH(H/ TOTAL)

RANGE i

CABBAGE HAI GAMMA HA-22 2

1.35E+01

< LLD (0 /1 )

< LLD

( 0 /1 )

1 (PCI/KG(WET))

1

< lid (0 /1 )

CABBAGE HAI GAMMA RU-106 2

1.13E+02

< LLD (0 /1 )

< LLD

( 0 /1 )

1 (PCI/KGtWET))

1

< LLD (0 /1 )

CABBAGE HAI GAMMA I-133 2

1.25E+01

< LLD (G /1 7

< LLD

( 0 /1 )

1 (PCI/KG(WET))

1

< LLD (0 /1 )

CABBAGE HAI GAMMA CS-137 2

1.25E+01

< LLD (0 /1 )

1 (PCI/KG(WET))

1

< LLP (0 /1 )

CORH

.HAI GAMMA CE-144 5

9.62E+01

< LLD (0 /4 )

< LLD (0 /1 )

1 2 3 4 (PCI/KG(WET))

4

< LID (0 /1 )

CORH HAI GAMMA AG-110M 5

1.92E+01

< LLD (0 /4 )

< LLD (0 /1 )

1 2 3 4

__ (PCI/KG(WET))

4

< LLD (0 /1 )

CORN HAI GAMMA TE-129M 5

4.20E+02

< LLD (0 /4 )

< LLD (0 /1 )

1 2 3 4 (PCI/KG(WET))

4

< LLD'(0 /1 )

t

- 1

.~

RADIOLOGICAL ENVIRONMENTAL MOHITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH JUNE,1982 THROUGH HOVEMBER,1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEANCH/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATI0HS USED OF RANGE RANGE FOR INDICATOR MEAH ANALYSES PERFORMED STATION STATION-MEAN(H/ TOTAL)

RANGE CORN HAI GAMMA MD-99 5

6.12E+03

< LLD (0'/4 )

< LLD (0 /1 )

1 2 3 4 (PCI/KG(WET))

4

< LLD (0 /1 )

4 CORM HAI GAMMA ZRH0-95 5

2.54E+01

< LLD (0 /4 )

< LLD (0 /1 )

1 2 3 4 (FCI/KG(WET))

4

< LLD (0 /1 )

l CORN HAI GAMMA CS-134 5

1.90E+01

< LLD (0 /4 )

< LLD (0 /1 )

1 2 3 4 (PCI/KG(WET))

1 4

< LLD (0 /1 )

CORN HAI GAMMA CD-58 5

2.16E+01

< LLD (0 /4 )

< LLD

( O /1 )

1 2 3 4 f

(PCI/KG(WET))

9

< L L D ( 0 /1 )

CORH HAI GAMMA MH-54 5

2.24E+01

< LLD (0 /4 )

< ( LD (0 /1 )

1 2 3 4 (PCI/KG(WET))

4

< LLD (0 /1 )

CORN HAI GAMMA TH-232 5

8.38E+01

< LLD (0 /4 )

< L LD (0 /1 )

1 2 3 4 (PCI/KG(WET))

4

< LLD (G /1 )

CORN HAI GAMMA FE-59 5

5.90E+01

< LLD (0 /4 )

< LLD (O /1 )

1 2 3 4 (PCI/KG(WET))

4

< LLD (0 /1 )

- )

9 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE.1982 THROUGH NOVEMBER,1982 SEMI-AHHUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(N/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATIDH STATION-MEAH(N/ TOTAL)

RANGE CORN HAI GAMMA CS-136 5

6.88E+01

< LLD (0 /4 )

< LLD (0/11 1 2 3 4 (PCI/KG(WET))

4

< LLD (0 /1 )

CORN HAI GAMMA TE-132 5

3.78E+02

< LLD (0 /4 )

< LLD (0/13 1 2 3 4 (PCI/KG(WET))

4

< LLD (0 /1 )

CORH HAI GAMMA ZH-65 5

5.86E+01

< LLD (0 /4 )

< LLD (0 /1 3 1 2 3 4 (PCI/KG(WET))

4

< LLD (0 /1 )

CORH HAI GAMMA Co-60 5

2.50E+01

< LLD (0 /4 )

< LLD (0 /1 )

1 2 3 4 (PCI/KG(WET))

4

< LLD (0 /1 )

CORH HAI GAMMA K-40 5

4.70E+02 2.90E+03 (4 /4 3 3.30E+03(1 /1 3 1 2 3 4

( PC I/ KG( WE T )')

( 2.40E+03 - 3.40E+03)

( 3.30E+03 - 3.30E+03) 4 3.40E+03(1 /1 )

( 3.40E+03 - 3.40E+03)

CORN HAI GAMMA BALA-140 5 6.28E+01

< LLD (0 /4 )

< LLD (0/13 1 2 3 4 (PCI/KG(WET))

4

< LLD (0 /1 )

CORM HAI GAMMA BE-7 5

1.88E+02

< LLD (0 /4 )

< LLD

( 0 /1 )

1 2 3 4 (PCI/KGtWET))

"~

4

< LLD (0 /1 ) 5

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE.1982 THROUGH NOVEMBER,1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICA 10R-MEAN(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICAIOR MEAN ANALYSES PERFORMED STATION STATIDH-MEAH(H/ TOTAL)

RANGE CORN HAI GAMMA CR-51 5

2.10E+02

< LLD (0 /4 )

< LLD (0 /1 )

1 2 3 4 (PCI/KG(WET))

4

< LLD (0 /1 )

CORN HAI GAMMA RA-226 5

3.74E+01

< LLD (0 /4 )

< LLD (0 /1 )

1 2 3 C (PCI/KG(WET))

4

< LLD (0 /1 )

CORN HAI GAMMA I-131 5

5.62E+01

< LLD (0 /4 )

< LLD (0 /1 )

1 2 4

(PCI/KG(WET))

4

< LLD (0 /1 )

CORN HAI GAMMA HA-22 5

2.50E+01

< LLD (0 /4 )

< LLD (0/13 1 2 3 4 (PCI/KG(WET))

4

< LLD (0 /1 )

CORH HAI GAMMA RU-106 5

1.92E+02

< LLD (0 /4 )

< LLD (0 /1 1 1 2 3 4 (PCI/KG(WET))

4

< LLD (0 /1 )

CORN HAI GAMMA I-133 5

2.50E+01

< LLD (0 /4 )

< LLD (0 /1 )

1 2 3 4 (PCI/KG(WET))

4

<,LLD (0 /1 )

CORN HAI GAMMA CS-137 5

2.20E+01

< LLD (0 /4 )

< LLD (0/13 1 2 3 4 (PCI/KG(WET))

4'

< LLD (0 /1 )

. 1

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH JUKE.1982 THROUGH NOVEMBER,1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED 0F RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATION STATIDH-MEAH(H/ TOTAL)

RANGE CUCUMBERS HAI GAMMA CE-144 1

1.60E+01

< LLD (0 /1 )

(.

/. )

5

)

(PCI/KG(WET))

(

5

< LLD (0 /1 )

CUCUMBERS HAI GAMMA AG-110M 1

6.50E+00

< LLD (0 /1 )

C. /. )

5

)

(PCI/KG(WET))

(

5

< LLD (0 /1 )

CUCUMBERS HAI GAMMA TE-129M 1

1.30E+02

< LLD (0 /1 )

(.

/. )

5 (PCI/KG(WET))

(

)

5

< LLD (0 /1 )

CUCUMBERS NAI GAMMA MO-99 1

2.40E+03'

< LLD (0 /1 )

(.

/. )

5 (PCI/KG(WET))

(

)

5

< LLD (0 /1 )

CUCUMBERS HAI GAMMA ZRH8-95 1

7.30E+00

< LLD (0 /1 )

(. /. )

5 (PCI/KG(WET))

(

)

5

< LLD (0 /1 )

CUCUMBERS MAI GAMMA CS-134 1

6.30E+00

< LLD (O /1 )

(.

/. )

5 (PCI/KG(WET))

(

)

5

< LLD (0 /1 )

CUCUMBERS HAI GAMMA CD-58 1

7.20E+00

< LLD (p /1 )

(.

/. )

5 (PCI/KG(WET))

(

)

5

< LLD (0 /1 )

- i i

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GEHERATING STATION JUNE,1982 THROUGH NOVEMBER.1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATIDH STATIDH-MEAH(H/ TOTAL)

RANGE

(.

/. )

5 CUCUMBERS HAI GAMMA MN-54 1

6.40E+00

< LLD

( O /1 )

)

(PCI/KG(WET))

(

5

< LLD (0 /1 )

CUCUMBERS HAI GAMMA TH-232 1

3.10E+01

< LLD (0 /1 )

(.

/. )

5

)

(PCI/KG(WET))

(

5

< LLD (0 /1 )

CUCUMBERS HAI GAMMA FE-59 1

1.80E+01

< LLD (0 /1 )

(.

/. )

5 (PCI/KG(WET))

(

)

5

< LLD (0 /1 )

CUCUMBERS NAI GAMMA CS-136 1

2.20E+01

< LLD (O /1 )

(.

/. )

5 (PCI/KGtWET))

(

)

5

< LLD (0 /1 )

CUCUMBERS HAI GAMMA TE-132 1

9.00E+01

< LLD

( 0 /1 )

(.

/. )

5 (PCI/KG(WET))

(

)

5

< LLD (0 /1 )

CUCUNBERS HAI GAMMA ZH-65 1

1.60E+01

< LLD (0 /1 )

(.

/. )

5 (PCI/KG(WET))

(

)

5

< LLD (0 /1 )

CUCUMBERS HAI GAMMA CD-60 1

6.20E+00

< LLD (0 /1 )

(.

/. )

5 (PCI/KG(WET))

(

)

5

< LLD (0 /1 )

k

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GEHERATING STATIDH JUNE,1982 THROUGH NOVEMBER.1982 SEMI-ANNUAL

SUMMARY

I SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIGHS USED DF RANGE RANGE FOR INDICAIOR MEAN ANALYSES PERFORMED STATI0H STATI0H-MEAH(N/ TOTAL)

RANGE CUCUMBERS HAI GAMMA K-40 1

1.60E+02 1.40E+03 (1 /1 )

(.

/. )

5

)

(PCI/KG(WET))

( 1.40E+03 - 1.40E+03)

(

F 5

1.40E+03(1 /1 )

( 1.40E+03 - 1.40E+03)

CUCUMBERS HAI GAMMA BALA-140 1 1.50E+01

< LLD (0 /1 )

C. /. )

5 (PCI/KG(WET))

(

)

5

< LLD (0 /1 )

CUCUMBERS HAI GAMMA BE-7 1

5.70E+01

< LLD (0 /1 )

(.

/. )

5 (PCI/KG(WET))

(

)

5

< LLD (0 /1 )

o CUCUMBERS HAI GAMMA CR-51 1

4.60E+01

< LLD

( 0 /1 )

(.

/. )

5 (PCI/KG(WET))

(

)

5

< LLD (0 /1 )

CUCUMBERS HAI GAMMA RA-226 1

1.10E+01

< LLD (0 /1 )

(, /. )

5 (PCI/KG(WET))

(

)

i 5

< LLD (0 /1 )

__ CUCUMBERS HAI GAMMA I-131 1

1.80E+01

< LLD (0 /1 )

(.

/, )

5 (PCI/KG(WET))

(

)

5

< LLD (0 /1 )

CUCUMBERS NAI GAMMA HA-22 1

6.30E+00

< LLD (0 /1 )

C. /. )

5 (PCI/KG(WET))

(

)

"I 5

< LLD (0 /1 ) l

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK NUCLEAR GENERATING STATIDH JUNE.1982 THROUGH NOVEMBER,1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAN(H/ TOTAL)

B ACKROUND-MEAN(H/ TOT AL )

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATION STATION-MEAH(N/ TOTAL)

RA:lGE CUCUMBERS HAI GAMMA RU-106 1

6.40E+01

< LLD (0 /1 )

(.

/.

5

)

(PCI/KG(WET))

(

5

< LLD (0 /1 )

CUCUMBERS NAI GAMMA I-133 1

6.20E+00

< LLD (0 /1 )

C. /. )

5

)

(PCI/KG(WET))

(

5

< LLD (0 /1-)

CUCUMBERS HAI GAMMA CS-137 1

6.20E+00

< LLD (0 /1 )

C. /. )

5

)

(PCI/KG(WET))

(

I 5

< LLD (0 /1 )

SURFACE WATER GROSS ALPHA-SS 48 1.01E+00

< LLD (0 /42 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/L

)

32 33 33

< LLD (0 /6 )

SURFACE WATER GROSS ALPHA-LS 48 3.77E-01 1.58E+00 (39 /42 )

2.08E+00(6 /6 3 23 24 25 26 27 (PCI/L

)

( 4.50E 2.78E+00)

( 1.61E*00 - 3.03E+00) 32 33 25 1.93E+00(6 /6 )

( 1.43E+00 - 2.54E+00)

SURFACE WATER GROSS BETA-SS 48 1.34E+00 9.29E-01 (1 /42 )

< LLD (0 /6 )

23 24 25 26 27

~~

(PCI/L

)

( 9.29E 9.29E-01) 32 33

'32 9.29E-01(1 /6 )

( 9.29E 9.29E-01)

SURFACE WATER GROSS BETA-DS 48 1.73E+01 1.59E+02 (36 /42 )

2.29E+02(6 /6 )

23 24 25 26 27 (PCI/L

)

( 2.24E+00 - 2.94E+02)

( 1.87E+02 - 2.76E+02) 32 33

~

25 2.07E+02(6 /6 )

( 1.16E*02 - 2.94E*02) 1

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH JUNE.1982 THROUGH HOVEMBER,1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(N/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATION STATION-MEAH(H/ TOTAL)

RANGE SURFACE WATER CALCIUM BY AA 48 2.00E-01 1.86E+02 (42 /42 )

2.91E+02(6 /6 3 23 24 25 26 27 (MG/L

)

( 1.00E 3.50E+02)

( 1.20E+02 - 3.60E*02) 32 33 24 2.69E+02(6 /6 )

( 1.15E+02 - 3.50E+02)

SURFACE WATER TRITIUM 48 1.62E+02

< LLD (0 /42 3

< LLD (0 /6 )

23 24 25 26 27 (PCI/L

)

32 33 33

< LLD (0 /6 )

SURFACE WATLR 10 DINE-131 24 1.38E-01

< LLD (O /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 33

< LLD (0 /3 )

SURFACE WATER HAI GAMMA CE-144 48 5.78E+01

< LLD (0 /42 )

< LLD (0 /6 3 23 24 25 26 27 (PCI/L

)

32 33 33

< LLD (0 /6 )

SURFACE WATER HAI GAMMA AG-110M 48 5.71E+00

< LLD (0 /42 )

< LLD (0 /6 3 23 24 25 26 27 (PCI/L

)

32 33 33

< LLD (0 /6 )

SURFACE WATER HAI GAMMA TE-129M 48 1.13E+02

< LLD (0 /42 3

< LLD (0 /6 3 23 24 25 26 27 (PCI/L

)

32 33 33

< LLD (0 /6 )

SURFACE WATER HAI GAMMA MD-99 48 1.44E+03

< LLD (0 /42 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/L

)

32 33 33

< LLD (0 /6 )

, I

RADIOLOGICAL ENVIRONNEHTAL MONITORING PROGRAN

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE,1982 THROUGH NOVEMBER,1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAN(N/ TOTAL)

BACKROUND-MEAH(N/7OTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATION STATION-MEAH(H/ TOTAL)

RANGE SURFACE WATER HAI GAMMA ZRH8-95 48 5.99E+00

< LLD (0 /42 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/L

)

32 33 33

< LLD (C /6 )

SURFACE WATER HAI GAMMA CS-134 48 5.52E+00

< LLD (0 /42 )

< LLD (0 /6 3 23 24 25 26 27 (PCI/L

)

32 33 33

< LLD (0 #6 )

SURFACE WATER NAI GAMMA CO-58 48 5.9IE+00

< LLD (0 /42 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/L

)

32 33 33 9.LD (0 /6 )

SURFACE WATER HAI GAMMA MH-54 48 5.50E+00

< LLD (0 /42 3

< LLD (0 /6 )

23 24 25 26 27 (PCI/L 3

32 33 33

< LLD (0 /6 )

SURFACE WATER HAI GAMMA TH-232 48 2.04E+01

< LLD (0 /42 3

< LLD (0 /6 )

23 24 25 26 27 (PCI/L 3

32 33 33

< LLD (0 /6 )

SURFACE WATER HAI GAMMA FE-59 48 1.24E+01

< LLD (0 /42 )

< LLD (0 /6 3 23 24 25 26 27 (PCI/L

)

32 33 33

< LLD (0 /6 )

SURFACE WATER HAI GAMMA CS-136 48 1.50E+01

< (LD (0 /42 )

< LLD (0 /6 3 23 24 25 26 27 (PCI/L

)

32. 33 33

< LLD (0 /6 ) L-

RADIOLOGICAL ENVIRONMENTAL MONI10 RING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE.1982 THROUGH HOVEMBER 1982 SEMI-AMNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE NUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED 0F RANGE RANGE FOR INDICA 10R MEAL

ANALYSES PERFORMED STATION STATIOM-MEAH(N/ TOTAL)

RANGE l

l l

SURFACE WATER tiAI GAMMA TE-132 48 1.87E+02

< LLD (0 /42 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/L

)

32 33 1

33

< LLD (0 /6 )

l

)

i SURFACE WATER HAI GAMMA ZN-65 48 1.21E+01

< LLD (0 /42 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/L

)

32 33 33

< LLD (0 /6 )

1 3URFACE WATER HAI GAMMA CO-60 48 5.64E+00

< LLD (0 /42 )

< t LD (0 /6 )

23 24 25 26 27 (PCI/L 3

32 33 33

< LLD (e /6 3 SURFACE WATER HAI GAMMA K-40 48 8.41E+01 3.16E+02 (31 /42 )

3.10E+02(6 /6 3 23 24 25 26 27 (PCI/L 3

( 6.30E+01 - 2.60E+03)

( 2.30E+02 - 3.90E+02) 32 33 25 6.18E+02(6 /6 )

I

( 2.10E+02 - 2.60E+03) i SURFACE WATER NAI GAMMA BALA-140 48 1.36E+01

< LLD (0 /42 )

< LLD (0 /6 )

23 24 25 26 27

+

(PCI/L

)

32 33 33

< LLD (0 /6 )

"" SURFACE WATER HAI GAMMA BE-7 48 5.92E+01

< LLD (O /42 3

< LLD (0 /6 3 23 24 25 26 27 (PCI/L

)

32 33 33

< LLD (0 /6 )

SURFACE WATER HAI GAMMA CR-51 48 7.50E+01

< LLD (0 /42 3

< LLD (0 /6 )

23 24 25 26 27 (PCI/L

)

32 53

~Z 33

< LLD (0 /6 ) l

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE.1982 THROUGH NOVEMBER,1982 SEMI-AHHUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMOER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(N/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATION STATIDH-MEAH(H/ TOTAL)

RANGE 3URFACE WATER HAI GAMMA RA-226 48 1.04E*01

< LLD (0 /42 )

< LLD (0 /6 3 23 24 25 26 27 (PCI/L

)

32 33 33

< LLD (0 /6 )

SURFACE WATER H&I GAMMA I-131 48 2.09E+01

< LLD (0 /42 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/L 3

32 33 33

< LLD (0 /6 )

SURFACE WATER HAI GAMMA HA-22 48 5.74E+00

< LLD (O /42 )

< LLD (O /6 )

23 24 25 26 27 (PCI/L

)

32 33 a

33

< LLD (0 /6 )

SURFACE WATER HAI GAMMA RU-106 48 5.60E+01

< LLD (0 /42 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/L

)

32 33 33

< LLD (0 /6 )

SURFACE WATER HAI GAMMA I-133 48 6.64E+00

< LLD (0 /42 3

< LLD (0 /6 )

23 24 25 26 21 (PCI/L

)

32 33 33

< LLD (0 /6 )

SURFACE WATER HAI GAMMA CS-137 48 5.89E*00

< LLD (0 /42 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/L

)

32 33 33

< LLD (0 /6 )

l SURFACE WATER RADIUM-226 48 7.99E-02 3.07E-01 (29 /42 )

1.28E-01(4 /6 )

23 24 25 26 27 (PCI/L

)

( 4.53E 7.25E-01)

( 4.63E 1.90E-01) 32 33 26 5.20E-01(5 /6 )

( 3.75E 6.81E-01) t

.~

i l

l RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK NUCLEAR GENERATING STATIDH JUNE.1982 THROUGH NOVEMBER,1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE NUMOER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAN(N/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATION STATION-MEAN(N/ TOTAL)

RANGE SURFACE WATER RADIUM-228 48 1.13E+00 5.39E-01 (1 /42 3

< LLD (0 /6 3 23 24 25 26 27 (PCI/L

)

( 5.39E 5.39E-01) 32 33 6

27 5.39E-01(1 /6 )

( 5.39E 5.39E-01)

SURFACE WATER STRONTIUM-89 48 5.90E-01 3.89E-01 (3 /42 3

< LLD (0 /6 3 23 24 25 26 27 (PCI/L

)

( 3.64E 4.18E-01) 32 33 25 4.18E-01(1 /6 )

( 4.18E 4.18E-01)

SURFACE WATER STRONTIUM-90 48 5.55E-01

< LLD (0 /42 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/L

)

32 33

'LLD (0 /6 )

33 i

SURFACE WATER TOTAL URANIUM 48 1.50E-01 1.10E+00 (41 /42 )

1.47E+00(6 /6 3 23 24 25 26 27 i

(PCI/L

)

( 2.60E 1.98E*00)

( 1.13E+00 - 1.83E+003 32 33 i

25 1.52E+00($ /6 3

( 1.03E+PO - 1.89E*00)

GREEN BEANS NAI GAMMA CE-144 2

6.50E+01

(.

/. )

< LLD (0 /2 )

(PCI/KG(WET))

(

)

i

(.

/. )

(

)

GREEN BEANS NAI GAMMA AG-110M 2

1.55E+01

(.

/. )

< LLD (O /2 )

(PCI/KG(WET))

(

)

a

(.

/. )

(

)

7 l

-r-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK NUCLEAR GENERATING STATION JUNE.1982 THROUGH HOVEMBER,1982 SEMI-ANNUAL

SUMMARY

3 AMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICAIOR MEAN ANALYSES PERFORMED STATION STATIDH-MEAN(H/ TOTAL) i RANGE e

GREEN BEANS NAI GAMMA TE-129M 2

3.35E+02

(.

/. )

< LLD (0 /2 )

3 (PCI/KG(WET))

(

(.

/. )

)

(

GREEH BEANS NAI GAMMA MO-99 2

8.65E+03

(.

/. )

< LLD (0 /2 )

(PCI/KG(WET))

(

)

(.

/. )

3

(

GREEN BEANS HAI GAMMA ZRHB-95 2

1.80E+01

(.

/. )

< LLD (0 /2 )

(PCI/KG(WET))

(

)

C. /. )

)

(

GREEN BEANS HAI GAMMA CS-134 2

1.50E+01

(.

/. )

< LLD (0 /2 )

(PCI/KG(WET))

(

)

C. /. )

(

3 GREEN BEANS HAI GAMMA CD-58 2

1.75E+01

(. /. )

< LLD (0 /2 )

(PCI/KG(WET))

(

)

C. /. )

(

)

1 GREEN BEANS HAI GAMMA MH-54 2

1.60E*01

(.

/. )

< LLD (0 /2 )

(PCI/KG(WET))

(

)

(.

/. )

(

)

- I i

RADIOLOGICAL ENVIRONMEHTAL MONITORING PROGRAM

SUMMARY

OYSTER CREFK HUCLEAR GENERATING STATIDH JUNE 1982 THROUGH NOVEt1BER,1982 SEMI-AHHUAL'

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED 1

0F RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATIDH STATION-MEAH(H/ TOTAL)

RANGE GREEN BEANS HAI GAMMA TH-232 2

7.00E+01 C./.

)

< LLD (0 /2 )

)

(PCI/KG(WET))

(

(.

/. )

)

(

GREEN BEANS HAI GAMMA FE-59 2

4.05E+01

(.

/. )

< LLD (0 /2 )

(PCI/KG(WET))

(

)

(.

/. 3

)

(

i GREEN BEANS HAI GAMMA CS-136 2

5.95E+01

(.

/. )

< LLD (0 /2 )

(PCI/KG(WET))

(

)

i

(.

/. )

(

)

GREEN BEANS HAI GAMMA TE-132 2'

4.60E+02

(.

/. )

< LLD (O /2 )

(PCI/KG(WET))

(

)

C. /. )

(

3 GREEN BEANS HAI GAMMA ZH-65 2

4.10E+01

(.

/. )

< LLD (D /2 )

(PCI/KG(WET))

(

)

d P

(- #-

)

g

)

GREEH BEANS HAI GAMMA CO-60 2

1.60E+01

(.

/. )

< LLD (0 /2 )

(PCI/PS(WET))

(

)

(.

/. )

(

)

= I

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK NUCLEAR GENERATING STATIDH JUNE.1982 THROUGH NOVEMBER 1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATION STATIDH-MEAH(H/ TOTAL)

RANGE i

GREEH BEAHS NAI GAMMA K-40 2

3.10E+02

(.

/. )

1.80E+03(2 /2 )

)

( I.70E+03 - 1.90E+03)

(PCI/KG(WET))

(

(.

/. )

)

(

GREEN BEANS HAI GAMMA BALA-140 2 4.00E+01

(.

/. )

< LLD (0 /2 )

)

(PCI/FG(WET))

(

(.

/. )

)

(

GREEN BEANS HAI GAMMA BE-7 2

1.70E+02

(.

/. )

< LLD (O /2 )

)

(PCI/KG(NET))

(

(.

/. )

)

(

GREEH BEANS NAI GAMMA CR-51 2

1.70E+02

(.

/. )

< LLD (0 /2 3

)

(PCI/KG(WET))

(

C. /. )

)

(

GREEN BEAHS HAI GAMMA RA-226 2

3.10E+01

(.

/. )

< LLD (O /2 )

(PCI/KG(WET))

(

)

(,

/. )

GREEH BEANS HAI GAMMA I-131 2

6.30E+01

(.

/. )

< LLD (0/23 (PCI/KG(WET))

(

)

(.

/. )

)

(

- 1

RADIOLOGICAL ENVIRONMENTAL MOHITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GEHERATING STATIDH JUNE,1982 THROUGH HOVEMBER,1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE AHALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATI0HS USED OF RANGE RANGE FOR INDICATOR MEAH AHALYSES PERFORMED STATIDH STATIDH-MEAH(N/ TOTAL)

RANGE 1

GRFEH BEANS HAI GAMMA HA-22 2

1.60E+01

(.

/. )

< LLD (0 /2 )

)

(PCI/KG(WET))

(

(.

/. )

)

(

GREEN BEANS HAI GAMMA RU-106 2

1.50E+02

(.

/. )

< LLD (0 /2 )

(PCI/KG(WET))

(

)

i

(.

/. )

)

(

GREEH BEANS HAI GAMMA I-133 2

1.60E+01

(.

/. )

< LLD (0 /2 )

)

(PCI/KG(WET))

(

l

(.

/. )

)

i

(

GREEH BEANS HAI GAMMA CS-137 2

1.60E+01

(.

/. )

< LLD (O /2 )

(PCI/KG(llET))

(~

)

(.

/. )

(

)

TDMATOES HAI GAMMA CE-144 6

2.42E+01

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

5

< LLD (0 /1 )

TOMATOES HAI GAMMA AG-110M 6

8.97E+00

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

5

< LLD (0 /1 )

~~

- I

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK NUCLEAR GENERATING STATION JUNE.1982 THROUGH HOVEMBER,1982 SEMI-AHHUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/T0!AL)

BACKROUND-MEAh!N/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATION STATIDH-MEAH(H/ TOTAL)

RANGE TOMATOES NAI GAMMA TE-129M 6

1.68E+02

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

5

< LLD (0 /1 )

TOMATOES HAI GAMMA MD-99 6

3.10E+03

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

5

< LLD (0 /1 )

TDMATOES HAI GAMMA ZRHB-95 6

1.04E+01

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

5

< LLD (0 /1 )

TDMATOES HAI GAMMA CS-134 6

9.23E+00

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

5

< LLD (0 /1 )

TOMATOES HAI GAMMA CD-58 6

1.05E+01

< LLD (0 /4 )

< LLD (0/23 2 3 4 5 (PCI/KG(WET))

5

< LLD (0 /1 )

TOMATOES HAI GAMMA MN-54 6

9.35E+00

< LLD (0 /4 )

< LLD (0 /2 3 2 3 4 5

__ (PCI/KG(WET))

5

< LLD (0 /1 )

TOMATOES HAI GAMMA TH-232 6

3.88E+01

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

5

< LLD (0 /1 )

9 ?

4

a I

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE.1982 THROUGH HOVEMBER,1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(N/ TOTAL)

STATI0HS USED OF RANGE RANGE FOR INDICATOR MEAH ANALYSES PERFORMED STATIDH STATIDH-MEAH(H/ TOTAL)

RANGE TOMATOES HAI GAMMA FE-59 6

2.32E+01

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

5

< LLD (0 /1 )

TDMATOES HAI GAMMA CS-136 6

2.73E+01

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

5

< LLD (O /1 )

TOMATOES HAI GAMMA TE-132 6

1.51E+02

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KGtWET))

5

< LLD (0 /1 )

TDMATOES HAI GAMMA ZH-65 6

2.42E+01

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

5

< LLD (0 /1 )

T0MATOES HAI GAMMA CD-60 6

9.45E+00

< LLD (0 /4 )

< LLD (0/23 2 3 4 5 (PCI/KG(WET))

4 5

< LLD (0 /1 )

TOMATOES HAI GAMMA K-40 6

2.10E+02 2.02E+03 (4 /4 3 2.15E+03(2 /2 )

2 3 4 5

__ (PCI/KG(WET))

( 1.80E+03 - 2.40E+03)

( 1.80E+03 - 2.50E+03) 2 2.40E+03(1 /1 )

( 2.40E+03 - 2.40E+03)

TDMATOES HAI GAMMA BALA-140 6 2.15E+01

< LLD (0 /4 )

< LLD (0 /2 3 2 3 4 5 (PCI/KG(WET))

"2 5

< LLD (0 /1 )

r RADIOLOGICAL ENVIRONMENTAL M0HITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE.1982 THROUGH HOVEMBER,1982 SEMI-AHHUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE NUMBER LLD INDICATOR-MEAH(N/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOP. MEAf8 i

ANALYSES PERFORMED STATIDH STATI0H-hEAH(H/ TOTAL)

RANGE TOMATOES HAI GAMMA BE-7 6

S.45E*01

< LLD (O /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KGtWET))

5

< LLD (0 /1 )

TOMATOES HAI GAMMA CR-51 6

7.93E+01

< LLD (0 /4 )

< LLD (O/23 2 3 4 5 (PCI/KG(WET))

5

< LLD (0 /1 )

TDMATOES MAI GAMMA RA-226 6

1.62E+01

< LLD (0 /4 )

< LLD (0 /2 3 2 3 4 5 (PCI/KG(WET))

5

< LLD (0 /1 )

TOMATOES HAI GAMMA I-131 6

2.72E+01

< LLD (0 /4 )

< LLD (O/23 2 3 4 5 (PCI/KG(WET))

5

< LLD (0 /1 )

TOMATOES HAI GAMMA HA-22 6

1.05E+01

< LLG (0 /4 )

< LLD (0 /2')

2 3 4 5 (PCI/KG(WET))

5

< LLD (0 /1 )

TOMATOES HAI GAMMA

.RU-IO6 6

8.30E+01

< LLD (8 /4 )

< LLD (O /2 3 2 3 4 5 (PCI/KG(WET))

5

< LLD (0 /1 )

TOMATOES MAI GAMMA I-133 6

9.15E+00

< LLD (O /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

4 5

< LLD (0 /1 )

- l

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE.1982 THROUGH NOVEMBER,1982 SEMI-AHHUAL

SUMMARY

SAMPLE TYPE AMALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDMS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATION STATION-MEAH(H/ TOTAL)

RANGE TOMATOES NAI GAMMA CS-137 6

9.7 0 E+ 0 0

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

5

< LLD (0 /1 )

WELL WATER GROSS ALPHA-SS 36 8.22E-Ol 3.34E-Ol (1 /36 )

(.

/. )

1 18 19 20 21

)

22 (PCI/L

)

( 3.34E 3.34E-Ol)

(

1 3.34E-01(1 /6 )

( 3.34E 3.34E-01)

WELL WATER GROSS ALPHA-DS 36 2.04E+00 3.94E*00 (14 /36 )

(. /. )

1 18 19 20 21 (PCI/L

)

( 6.99E 9.32E+00)

(

)

22 19 5.29E+00(3 /6 )

( 2.10E+00 - 9.32E+00)

WELL WAIER GROSS BETA-SS 36 7.79E-01 6.31E-01 (1 /36 )

(. /. )

1 18 19 20 21 (PCI/L

)

( 6.31E-Ol - 6.31E-01)

(

3 22 22 6.31E-01(1 /6 )

( 6.31E 6.31E-01)

WELL WATER GROSS BETA-DS 36 1.03E+00 2.51E+00 (30 /36 )

(.

/. )

1 18 19 20 21 (PCI/L

)

( 1.08E*00 - 4.76E+00)

(

)

22 21 2.85E+00(5 /6 )

( 1.67E+00 - 4.76E+00)

WELL WATER POTASSIUM-40 12 8.60E-OI 1.51E+00 (7 /12 )

(.

/. )

1 18 19 20 21 (PCI/L

)

( l.21E+00 - 2.05E+00)

(

)

22 20 1.81E+00(2 /2 )

( 1.58E+00 - 2.05E+00)

T l

RADIOLOGICAL ENVIRONMENT AL MONITORING PROGRAM SUPW1ARY OYSTER CREEK HUCLEAR GENERATING STATIDH JUNE 1982 THROUGH NOVEMOER,1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

OACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAN i

ANALYSES PERFORMED STATION STATIDH-MEAH(H/ TOTAL)

RANGE WELL WATER TRITIUM 12 1.59E+02

< LLD (0 /12 )

(. /. )

1 18 19 20 21

)

22 (PCl/L

)

(

22

< LLD (0 /2 )

s WELL IfATER HAI GAMMA CE-144 12 6.33E+01

< LLD (0 /12 )

(.

/. )

1 18 19 20 21

)

22

.l (PCI/L

)

(

22

< LLD (0 /2 )

WELL WATER HAI GAMMA AG-110M 12 6.76E+00

< LLD (0 /12 )

C. /. )

1 18 19 20 21 (PCI/L

)

(

)

22 22

< LLD (0 /2 )

WELL WATER HAI GAMMA TE-129M 12 1.17E+02

< LLD (0 /12 )

(. /. )

1 18 19 20 21 (PCI/L

)

(

)

22 22

< LLD (0 /2 )

J WELL WATER HAI GAMMA MO-99 12 3.55E+02

< LLD (0 /12 )

(. /. )

1 18 19 20 21 (PCI/L

(

)

22 22

< LLD (0 /2 )

WELL WATER HAI GAMMA ZRHO-95 12 6.25E+00

< LLD (0 /12 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

}

22

+

I 22

< LLD (0 /2 )

WELL WATER HAI GAMMA CS-134 12 6.17E+00

< LLD (0 /12 )

C. /. )

1 18 19 20 21 (PCI/L

)

(

)

22 22

< LLD (0 /2 )

3 !

t i

RADIOLOGICAL ENVIRONMENTAL MOHITORING PROGRAM

SUMMARY

t OYSTER CREEK HUCLEAR GENERATING STATION JUNE.1982 THROUGH NOVEMBER,1982 SEMI-AHHUAL

SUMMARY

SAMPLE TYPE AHALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATISHS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATION STATION-MEAH(H/ TOTAL)

RANGE s

WELL WATER HAI GAMMA CO-58 12 6.58E+00

< LLD (0 /12 )

(. /. )

1 18 19 20 21

)

22 (PCI/L

)

(

22

< LLD (0 /2 3 WELL WATER HAI GAMMA MH-54 12 6.04E+00

< LLD (0 /12 )

(.

/. )

1 18 19 20 21

)

22 (PCI/L 3

(

22

< LLD (0 /2 )

t WELL WATER HAI GAMMA TH-232 12 2.22E+01

< LLD (0 /12 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22 22

< LLD (0 /2 )

WELL WATER HAI GAMMA FE-59 12 1.27E401

< LLD (O /12 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22 22

< LLD (0 /2 3 4

WELL WATER HAI GAMMA CS-136 12 1.16E+01

< LLD (O /12 )

(.

/. )

1 18 19 20 21 j

(PCI/L

)

(

)

22 22

< LLD (0 /2 )

WELL WATER HAI GAMMA TE-132 12 4.48E+01

< LLD (0 /12 )

(. /. )

1 18 19 20 21 (PCI/L

)

(

)

22 22

< LLD (0 /2 )

WELL WATER HAI GAMMA ZH-65 12 1.34E+01

< LLD (0 /12 )

C. /. )

1 18 19 20 21 (PCI/L

)

(

)

22 22

< LLD (0 /2 )

i 1

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK NUCLEAR GENERATING STATION JUNE.1982 THROUGH NOVEMBER.1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAN(H/ TOTAL)

BACERDOND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATION STATION-MEAM(N/ TOTAL)

RANGE WELL WATER HAI GAMMA CD-60 12 6.73E+00

< LLD (0 /12 )

(.

/. )

1 18 19 20 21

)

22 (PCI/L 3

(

22

< LLD (0 /2 )

4 WELL WATER HAI GAMMA K-40 12 7.64E+01

< LLD (0 /12 )

(. /. )

1 18 19 20 21

)

22 (PCI/L

)

(

22

< LLD (0 /2 )

l WELL WATER HAI GAMMA BALA-140 12 9.70E+00

< LLD (0 /12 )

(. /. )

1 18 19 20 21 3

22 (PCI/L

)

(

22

< LLD (0 /2 )

WELL WATER HAI GAMMA BE-7 12 6.49E+01

< LLD (0 /12 )

(.

/. )

1 18 19 20 21 j

(PCI/L 3

(

)

22 22

< LLD (0 /2 )

WELL WATER MAI GAMMA CR-51 12 7.47E+01

< LLD (0 /12 )

(.

/. )

1 18 19 20 21 t

(PCI/L

)

(

)

22 i

22

< LLD (0 /2 )

WELL WATER HAI GAMMA RA-226 12 1.25E+01 2.65E+01 (2 /12 )

(.

/. )

1 18 19 20 21 (PCI/L

)

( 2.50E+01 - 2.80E+01)

(

)

22 19 2.80E+01(1 /2 )

( 2.80E+01 - 2.80E+01)

WELL WATER HAI GAMMA I-131 12 1.58E+01

< LLD (0 /12 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22 22

< LLD (0 /2 ) 1

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK NUCLEAR GENERATING STATIDH JUNE.1982 THROUGH NOVEMBER,1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(N/ TOTAL)

BACKROUND-MEAH(N/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATION STATIDH-MEAH(H/T0YAL)

RANGE WELL WATER HAI GAMMA HA-2?

12 6.51E400

< LLD (O /12 )

(,

/. )

1 18 19 20 21

)

22 (PCI/L

)

(

22

< LLD (0 /2 )

WELL WATER HAI GAMMA RU-106 12 6.17E401

< LLD (0 /12 )

(.

/. )

1 18 19 20 21

)

22 (PCI/L

)

(

22

< LLD (0 /2 )

i WELL WATER HAI GAMMA I-133 12 1.36E+03

< LLD (0 /12 )

(. /. )

1 18 19 20 21 (PCI/L

)

(

)

22 22

< LLD (0 /2 )

WELL WATER HAI GAMMA CS-137 12 7.00E+00

< LLD (0 /12 )

C. /. )

1 18 19 20 21 (PCI/L

)

(

)

22 22

< LLD (0 /2 )

WELL WATER RADIUM-226 12 7.81E-02 3.83E-01 (6 /12 )

(.

/. )

1 18 19 20 21 (PCI/L

)

( 1.66E 5.73E-01)

(

)

22 19 5.73E-01(1 /2 )

( 5.73E 5.73E-01)

__ ELL WATER RADIUM-228 12 7.27E-01

< LLD (0 /12 )

(.

/. )

1 18 19 20 21 W

(PCI/L

)

(

)

22 l

22

< LLD (0 /2 )

WELL WATER TOTAL URANIUM 12 1.75E-01 4.28E-01 (12 /12 )

(.

/. )

1 18 19 20 21 (PCI/L

)

( 2.40E 7.70E-01)

(

)

22

~2 20 5.70E-01(2 /2 )

( 4.70E 6.70E-01) i I

=

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK NUCLEAR GENERATING STATION JUNE 19P<2 THROUGH NOVEMBER.1982 SEMI-ANNUAL

SUMMARY

S' AMPLE TYPE ANALYSIS ISOTOPE NUMBER LLD INDICATOR-MEAN(N/ TOTAL)

BACKROUND-MEAM(N/ TOTAL)

STATIONS USED OF-RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATIDH STATION-MEAM(N/ TOTAL)

RANGE CLAMS GROSS ALPHA 24 4.16E+01 1.51E+02 (15 /18 )

8.38E+01(6 /6 )

23 24 25 (PCI/KG(WET))

( 5.03E+01 - 3.57E+02)

( 4.50E+01 - 1.38E+02) 24 1.72E+02(5 /6 )

( 5.66E*01 - 3.57E+02)

CLAMS GROSS BETA 24 2.29E+01 9.18E+02 (18 /18 )

9.91E+02(6 /6 )

23 24 25 (PCI/KG(WET))

( 1.95E+02 - 1.39E*03)

( 6.55E*02 - 1.45E+03) 25 9.44E+02(6 /6 )

( 4.44E+02 - 1.39E+03)

CLAMS CALCIUM BY AA 8

2.60E-01 7.21E+01 (6 /6 )

7.65E+01(2 /2 )

23 24 25 (MG/GM(MET) )

( 3.00E+01 - 1.40E+02)

( 4.50E*01 - 1.08E+02) 25 9.59E+01(2 /2 )

( 5.00E+01 - 1.40E+02)

CLANS

.NAI GAMMA CE-144 8

1.13E+02

< LLD (0 /6 )

< LLD (0 /2 )

23 24 ' 25 (PCI/KG(WET))

25

< LLD (0 /2 )

CLAMS NAI GAMMA AG-110M 8

2.85E+01

< LLD (0 /6 )

< LLD (O /2 )

23 24 25 (PCI/KG(WET))

25

< LLD (0 /2 )

CLAMS NAI GAMMA TE-129M 8

6.19E+02

< LLD (0 /6 )

< LLD

( 0 /2 )

23 24 25 (PCI/KG(WET))

25

< LLD (0 /2 )

,_ CLAMS NAI GAMMA MD-99 8

1.94E+04

'< LLD (0 /6 )

< LLD (0 /2 )

23 24 25 (PCI/KG(WET))

i l

25

< LLD (0 /2 ) '

[

9

2--

u.-

RADIOLOGICAL ENVIRONMENTAL MOHITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE,1982 THROUGH NOVEMBER,1982 SEMI-ANNUAL

SUMMARY

3 AMPLE TYPE AHALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF GAMGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATION STATI0H-MEAN(H/ TOTAL)

RANGE CLANS HAI GAMMA ZRNB-95 8

3.09E+01

< LLD (0 /6 )

< LLD (0/23 23 24 25 (PCI/KG(WET))

25

< LLD (0 /2 )

CLANS HAI GAMMA CS-134 8

2.76E+01

< LLD (0 /6 )

< LLD (0 /? )

23 24 25 (PCI/KG(WET))

25

< LLD (0 /2 )

CLAMS HAI GAMMA CO-58 8

3.25E+01

< LLD (0 /6 )

< LLD (0 /2 )

23 24 25 (PCI/KG(WET))

73

< LLD (0 /2 )

CLAMS HAI GAMMA MH-54 8

2.83E+01

< LLD (0 46 )

< LLD (0 /2 )

23 24 25 (PCI/KG(WET))

25

< LLD (0 /2 )

CLANS HAI GAMMA TH-232 8

1.09E+02

< LLD (0 /6 )

< LLD (0 /2 )

23 24 25 (PCI/KG(WET))

25

< LLD (0 /2 )

CLAMS HAI GAMMA FE-59 8

7.75E+01

< LLD (0 /6 )

< LLD (0 /2 )

23 24 25 (PCI/KG(WET))

25

< LLD (0 /2 )

CLANS HAI GAMMA CS-136 8

1.07E+02

< LLD (0 /6 )

< LLD (0 /2 )

23 24 25 (PCI/KG(WET))

25

< LLD (0 /2 )

- l

RADIOLOGICAL ENVIRONMENIAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK NUCLEAR GENERATING STATION JUNE.1982 THROUGN HOWEMBER 1982 s

SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE NUMBER LLD INDICATOR-MEAN(H/ TOTAL)

BACKROUND-MEAH(N/ TOTAL)

STATIONS ULED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATION STATION-MEAN(N/ TOTAL)

RANGE l

CLANS NAI GAMMA TE-132 8

9.23E+02

< LLD (0 /6 3

< LLD (0 /2 )

23 21 25 (PCI/KG(WET))

25

< LLD (0 /2 )

CLAMS NAI GAMMA ZH-65 8

6.95E+01

< LLD (0 /6 )

< LLD (0 /2 3 23 24 25 (PCI/KG(WET))

25

< LLD (R /2 )

CLAMS NAI GAMMA CD-60 8

3.31E+01

< LLD (0 /6 )

< LLD (0/21 23 24 25 (PCI/KG(WET))

25

< LLD (0 /2 )

CLAMS NAI GAMMA K-40 8

4.29E+02 1.07E403 (5 /6 )

1.65E+03(2 /2 )

23 24 25 (PCI/KG(WET))

( 5.30E+02 - 1.80E+03)

( l.00E+03 - 2.30E+03) 24 1.38E+03(2 /2 )

( 9.50E+02 - 1.80E+03) 4 CLAMS NAI GAMMA BALA-140 8 8.80E+01

< LLD (0 /6 )

< LLD (0 /2 )

23 24 25 (PCI/KGtWET))

25

< LLD (0 /2 )

CLAMS NAI GAMMA BE-7 8

3.20E+02

< LLD (0 /6 )

< LLD (0 /2 )

23 24 25

~~

(PCI/KG(WET))

25-

< LLD (0 /2 )

CLAMS NAI GAMMA CR-51 8

2.74E+02

< LLD (0 /6 )

< LLD (0 /2 )

23 24 25 (PCI/KG(WET))

25

< LLD (0 /2 )

-100-

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIGN JUNE.1982 THROUGH HOVEMBER.1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE NUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAN(N/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAH ANALYSES PERFORMED STATIDH STATION-MEAN(H/ TOTAL)

RANGE I

CLANS HAI GAMMA RA-226 8

5.05E+01

< LLD (0 /6 )

< LLD (0 /2 3 23 24 2'

(PCI/KG(WET))

25

< LLD (0 /2 )

CLAMS NAI GAMMA I-131 8

1.33E+02

< LLD (0 /6 )

< LLD (0 /2 3 23 24 25 l

(PCI/KG(WET))

25

< LLD (0 /2 )

l l

CLAMS HAI GAMMA HA-22 8

3.15E+01

< LLD (0 /6 )

< LLD (b /2 )

23 24 25 (PCI/KG(WET))

25

< LLD (0 /2 )

CLAMS HAI GAMMA RU-106 8

2.80E+02

< LLD (0 /6 3

< LLD (0 /2 )

23 24 25 l

(PCI/KG(WET))

25

< LLD (0 /2 )

CLANS HAI GAMMA I-133 8

3.31E+01

< LLD (0 /6 )

< LLD (0 /2 )

23 24 25 (PCI/KG(WET))

25

< LLD (0 /2 )

CLANS HAI GAMMA CS-137 8

3.llE+01

< LLD (0 /6 )

< LLD (0 /2 3 23 24 25 (PCI/KGtWET))

25

< LLD (0 /2 )

CLANS STRONTIUM-89 8

2.89E*01

< LLD (0 /6 )

< LLD (0 /2 )

23 24 25 (PCI/KG(WET))

25

< LLD (0 /2 )

-101-l

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH JUNE,1982.THROUGH NOVEMBER,1982 SEMI-AHHUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

SACKROUND-MEAH(H/ TOTAL)

STATIONS USED 0F RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATIDH STATIDH-MEAH(H/ TOTAL)

RANGE CLAMS STRONTIUM-90 8

1.52E+01

< LLD (0 /6 )

< LLD (0 /2 )

23 24 25 (PCI/KG(WET))

25

< LLD (0 /2 )

SOIL GROSS BETA 30 1.69E+03 4.42E+03 (27 /30 )

C. /. )

1 2 3 4 5

)

(PCI/KGCDRY))

( 1.90E+03 - 9.46E*03)

(

2 5.76E403(6 /6 )

( 3.45E+03 - 8.47E+03)

SOIL GELI GAMMA CE-144 20 2.27E+02

< LLD (0 /20 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

5

< LLD (0 /4 )

SOIL GELI GAMMA AG-110M 20 8.19E+01

< LLD (0 /20 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

5

< LLD (0 /4 )

SOIL GELI GAMMA TE-129M 20 1.26E+03

< LLD (0 /20 )

(. /. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

5

< LLD (0 /4 )

SDIL GELI GAMMA MO-99 19 1.43E+03

< LLD (0 /19 )

(.

/. )

1 2 3 4 5

~~

(PCI/KG(DRY))

(

)

5

< LLD (O /4 )

SDIL GELI GAMMA ZRH0-95 le 4.13E*01

< LLD (0 /10 )

(. /. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

5:

5

< LLD (0 /2 )

-102-

... ~

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH JUNE,1982 THROUGH HOVEMBER,1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAN(H/ TOTAL)

BACKROUND-MEAN(N/ TOTAL)

STATIONS USED 0F RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATION STATIDH-MEAH(H/ TOTAL)

RANGE SOIL GELI GAMMA CS-134 20 4.09E+01

< LLD (0 /20 )

(.

/, )

1 2 3 4 5 (PCI/KG(DRY))

(

)

5

< LLD (0 /4 )

i SOIL GELI GAMMA CO-58 20 3.31E+01

< LLD (0 /20 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

5

< LLD (0 /4 )

SOIL GELI GAMMA MN-54 20 3.20E+01

< LLD (0 /20 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

5

< LLD (0 /4 )

SOIL GELI GAMMA TH-232 20 1.29E+02 3.06E+s2 (17 /20 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

( 1.6 0 E+ 02 - 6.50E+ 02)

(

)

5 3.85E+02(4 /4 )

( 1.90E+02 - 6.50E+02) i SDIL GELI GAMMA FE-59 20 6.73E+01

< LLD (0 /20 )

(.

/. )

1 2 3 4 5 j

(PCI/KG(DRY))

(

)

5

< LLD (0 /4 )

t I

__ SOIL GELI GAMMA CS-136 19 6.01E+01

< LLD (0 /19 )

(,

/, )

1 2 3 4 5 (PCI/KG(DRY))

(

)

5

< LLD (0 /4 )

SOIL GELI GAMMA ZH-65 ' 20 8.53E+01

< LLD (0 /20 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

5

< LLD (0 /4 )

-103-I

RADIOLOGICAL ENVIRONMENTAL MOHITORING PROGRAM

SUMMARY

DYSTER CREEK HUCLEAR GENERATING STATIDH JUNE.1982 THROUGH NOVEMBER,1982 SEMI-AHHUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUM 3ER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAH AHALYSES PERFORMED STATIDH STATI0H-MEAH(H/ TOTAL)

RANGE SOIL GELI GAMMA CD-60 20 4.17E+01 6.00E+01 (2 /20 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

( 6.00E+01 - 6.00E+01)

(

)

2 6.00E+01(1 /4 )

( 6.00E+01 - 6.00E+01)

SDIL GELI GAMMA K-40 20 4.24E+02 1.18E+03 (18 /20 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

( 2.20E+02 - 2.00E+03)

(

1 1.45E+03(4 /4 )

( 5.10E+02 - 1.90E+03)

(

SDIL GELI GAMMA BALA-140 20 7.llE+01

< LLD

.(0 /20 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

5

< LLD (0 /4 )

SOIL GELI GAMMA BE-7 20 4.40E+02

< LLD (0 /20 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

1 5

< LLD (0 /4 )

SOIL GELI GAMMA ZR-95 11 7.51E+01

< LLD (0 /11 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

5

< LLD (0 /2 )

~~ SOIL GELI GAMMA HB-95 11 1.04E+02

< LLD (0 /11 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))-

(

)

5

< LLD (0 /2 )

SOIL GELI GAMMA SB-125 20 1.01E+02

< LLD (0 /20 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

5

< LLD (0 /4 )

-104-1

(

RADIOLOGICAL ENVIROHNENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE,1982 THROUGH HOVEMBER,1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLO INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATIDH STATION-MEAH(H/ TOTAL)

RANGE l

e SDIL GELI GAMMA CE-141 20 1.38E+02

< LLD (0 /20 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

c' 5

< LLD (0 /4 )

SOIL GELI GAMMA RU-103 20 6.48E+01

< LLD (0 /20 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

5

< LLD (0 /4 )

SOIL GELI GAMMA CR-51 20 3.86E+02

< LLD (0 /20 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

(-

)

5

< LLD (0 /4 )

SOIL GELI GAMMA RA-226 20 8.28E+01 3.03E+02 (18 /20 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

( 1.20E+02 - 5.80E+02)

(

)

5 3.57E+02(4 /4 )

( 1.20E+02 - 5.80E+02)

SOIL GELI GAMMA I-131 20 1.22E+02

< LLD (0 /20 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

5

< LLD (0 /4 )

__Sull GELI GAMMA HP-239 15 1.32E+05

< LLD (0 /15 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

5

< LLD (0 /3 )

SOIL GELI GAMMA RU-106 20 2.90E+02

< LLD (0 /20 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

~2 5

< LLD (0 /4 )

-105-I

.=

l l

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH l

JUNE.1982 THROUGH NOVEMBER,1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICAIOR MEAM i

ANALYSES PERFORMED STATIDH STATIDH-MEAH(H/ TOTAL)

RANGE I

SDIL GELI GAMMA C0-57 20 2.67E+01

< LLD

'(O /20 )

(,

/, )

1 2 3 4 5 (PCI/KG(DRY))

(

)

l 5

< LLD (O /4 )

SDIL GELI GAMMA CS-137 20 4.59E+01 5.69E+02 (20 /20 )

(.

/. )

1 2 3 a 5 (PCI/KG(DRY))

( 4.10E+01 - 1.50E+03)

(

)

2 8.88E+02(4 4'4 )

( l.80E+02 - 1.50E+03)

PASTURE GROSS BETA 6

5.35E+01 3.10E+03 (6 /6 )

(.

/. )

28 29 30 (PCI/KG(WET))

( l.28E+03 - 4.53E+03)

(

)

30 3.83E*03(2 /2 )

1

( 3.13E+03 - 4.53E+03)

PASTURE CALCIUM BY AA 6

8.00E-02 1.21E+02 (6 /6 )

(.

/. )

28 29 30 (MG/GM(WET) )

( 4.00E+01 - 2.23E+02)

(

)

29 1.41E*02(2 /2 )

( 6.00E+01 - 2.23E+02)

PASTURE HAI GAMMA CE-144 6

2.82E+02

< LLD (0 /6 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

f 30

< LLD (0 /2 )

1 PASTURE HAI GAMMA AG-110M 6

8.52E+01

< LLD (0 /6 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

30

< LLD (0 /2 )

__ PASTURE HAI GAMMA TE-129M 6

1.82E+03

< LLD (0 /6 )

(.

/. )

28 29 30

- (PCI/KG(WET))

(

}

30

< LLD (0 /2 )

j

-106-

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE,1982 THROUGH HOVEMBER,1982 SEMI-AHMUAL

SUMMARY

S' AMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS U3ED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATIDH STATIDH-MEAH(H/ TOTAL)

RANGE PASTURE HAI GAM.1A MD-99 6

4.64E+04

< LLD (0 /6 )

(,

/. )

28 29 30

)

(PCI/KG(WET))

(

30

< LLD (0 /2 3 PASTURE HAI GAMMA ZRNB-95 6

8.68E+01

< LLD (0 /6 )

(,

/. )

28 29 30

)

(PCI/KG(WET))

(

30

< LLD (0 /2 )

l PASTURE HAI GAMMA CS-134 6

8.20E+01

< LLD (0 /6 )

C. /. )

28 29 30

)

(PCI/KG(WET))

(

30

< LLD (0 /2 )

PASTURE HAI G4MMA CO-58 6

9.90E+01

< LLD (0 /6 )

(.

/. ).

28 29 30

)

(PCI/KG(WET))

(

30

< LLD (0 /2 )

PASTURE HAI GAMMA MH-54 6

8.75E+01

< LLD (0 /6 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

30

< LLD (0 /2 )

PASTURE HAI GAMMA TH-232 6

3.03E+02

< LLD (0 /6 )

(.

/. )

28 29 30 (PCI/KG(NET))

(

)

30

< LLD (0 /2 )

j l

l PASTURE HAI GAMMA FE-59 6

2.42E+02

< LLD (0 /6 )

(.

/. )

28 29 30 2

(PCI/KG(WET))

(

)

30

< LLD (0 /2 )

-107-

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE.1982 THROUGH NOVEMBER,1982 SEMI-AHHUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATION STATION-MEAH(H/ TOTAL)

RANGE PASTURE HAI GAMMA CS-136 6

3.38E+02

< LLD (O /6 )

(.

/. )

28 29 30

)

(PCI/KG(WET))

(

30

< LLD (0 /2 )

PASTURE HAI GAMMA TE-132 6

2.41E+03

< LLD (0 /6 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

30

< LLD (0 /2 )

PASTURE HAI GAMMA ZH-65 6

1.92E+02

< LLD (0 /6 )

(.

/. )

28 29 30

)

(PCI/KG(WET))

(

30

< LLD (0 /2 )

PASTURE HAI GAMMA CD-60 6

9.18E+01

< LLD (0 /6 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

30

< LLD (0 /2 )

PASTURE HAI GAMMA K-40 6

1.17E+03 4.00E+03 (2 /6 )

C. /. )

28 29 30 (PCI/KG(WET))

( 3.80E+03 - 4.20E+03)

(

)

28 4.20E+03(1 /2 )

( 4.20E+03 - 4.20E+03)

__ PASTURE HAI GAMMA BALA-140 6 3.33E*02

< LLD (0 /6 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

30

< LLD (0 /2 )

PASTURE HAI GAMMA BE-7 6

8.75E+02

< LLD (0 /6 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

"E

(

'30

< LLD (0 /2 )

i i

-108-l g

i

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE.1952 THROUGH NOVEMBER 1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USES OF RANGE RANGE FOR INDICAIOR MEAN ANALYSES PERFORMED STATIDH STATIDH-MEAH(H/ TOTAL)

RANGE PASTURE HAI GAMMA CR-51 6

9.60E+02

< LLD (0 /6 )

(.

/. )

28 29 30'

)

(PCI/KG(WET))

(

30

< LLD (0 /2 )

(

PASTURE HAI GAMMA RA-226 6

1.71E+02

< LLD (0 /6 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

30

< LLD (0 /2 )

PASTURE HAI GAMMA I-131 6

5.32E+02

< LLD (0 /6 )

C. /. )

28 29 30

)

(PCI/KG(WET))

(

a 30

< LLD (0 /2 )

PASTURE HAI GAMMA HA-22 6

9.32E+01

< LLD (0 /6 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

30

< LLD (0 /2 )

PASTURE HAI GAMMA RU-106 6

8.12E+02

< LLD (0 /6 )

(.

/. )

28 29 37 (PCI/KG(WET))

(

)

30

< LLD (0 /2 )

PASTURE HAI GAMMA I-133 6

9.50E+01

< LLD (0 /6 )

(.

/. )

28 29 30

__ (PCI/KG(WET))

(

)

30

< LLD (0 /2 )

PASTURE HAI GAMMA CS-137 6

9.10E+01

< LLD (0 /6 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

30

< LLD (0 /2 )

7

-109-

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATI0H JUNE.1982 THROUGH HOVEMBER,1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUHD-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAH ANALYSES PERFORMED STATIDH STATIDH-MEAH(H/ TOTAL)

RANGE PASIURE STRONTIUM-89 6

4.45E*01

< LLD (0 /6 )

(. /. )

28 29 30

)

(PCI/KG(WET))

(

30

< LLD (0 /2 )

PASTURE STRONTIUM-90 6

3.04E+02

< LLD (0 /6 )

C. /. )

28 29 30

)

(PCI/KG(WET))

(

30

< LLD (0 /2 )

SEDIMENT GROSS ALPHA 16 3.69E+03 6.42E+03 (7 /14 )

< LLD (0 /2 )

23 24 25 26 27 (PCI/KG(DRY))

( 3.98E+03 - 1.29E+04) 32 33 33 9.29E+03(2 /2 )

( 5.69E+03 - 1.29E+04)

SEDIMENT GROSS BETA 16 2.50E+03

'8.36E+03 (10 /14 )

1.10E+04(2 /2 )

23 24 25 26 27 (PCI/KG(DRY))

( 1.63E+03 - 1.88E+04)

( 1.07E+04 - 1.13E+04) 32 33 33 1.70E+04(2 /2 )

( l.52E+04 - 1.88E+04)

SEDIMENT GELI GAMMA CE-144 40 2.44E+02 8.10E+01 (1 /34 )

< LLD (0 /6 3 23 24 25 26 27 (PCI/KG(DRY))

( 8.10E+01 - 8.10E+01) 32 33 32 8.10E+01(1 /6 )

( 8.10E+01 - 8.10E+01)

SEDINENT GELI GAMMA AG-110M 40 4.86E+01

< LLD (0 /34 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 33

< LLD,(0 /6 )

SEDIMENT GELI GAMMA TE-129M 40 1 72E+03.

< LLD (0 /34 )

< LLD (0 /6 3 23 24 25 26 27 (PCI/KG(DRY))

32 33' 33

< LLD (0 /6 )

-110-

mr.

RADIOLOGICAL. ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE.1982 THROUGH HOVEMBER 1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED STATION STATI0H-MEAH(N/ TOTAL)

RANGE 1

SEDIMENT GELI GAMMA MD-99 23 1.06E+03

< LLD (0 /20 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 33

< LLD (O /3 )

SEDIMENT GELI GAMMA ZRHB-95 20 4.25E+01

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 33

< LLD (0 /3 )

SEDIMENT GELI GAMMA CS-134 40 5.12E+01

< LLD (0 /34 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 33

< LLD (0 /6 )

SEDIMENT GELI GAMMA CO-58 40 5.60E+01

< LLD (0 /34 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 33

< LLD (0 /6 )

SEDIMENT GELI GAMMA MH-54 40 4.93E+01 7.60E+01 (4 /34 )

< LLD (0 /6 ) '

23 24 25 26 27 (PCI/KG(DRY))

( 3.50E+01 - 1.20E+02) 32 33 i

33 8.83E+01(3 /6 )

( 3.50E+01 - 1.20E+02)

""SEDINENT GELI GAMMA TH-232 40 1.61E+02 3.94E+02 (28 /34 )

3.45E+02(6 /6 3 23 24 25 26 27 (PCI/KG(DRY))

( l.80E+02 - 7.60E+02)

( 2.60E+02 - 4.00E+02) 32 33 33 6.03E+02(6 /6 )

( 4.30E+02 - 7.60E+02)

SEDIMENT GELI GAMMA FE-59 40 1.46E+02

< LLD (0 /34 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/KG(DRY))'

32 33 33

< LLD (0 /6 )

-111-l L---

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GEHERATING STATIDH JUNE,1982 THROUGH NOVEMBER,1982 e

SEMI-AHHUAL

SUMMARY

SAMPLE TYPE AHALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR NEAH ANALYSES PERFORMED STATIDH STATI0H-MEAH(H/ TOTAL)

RANGE SEDIMENT GELI GAMMA CS-136 40 1.03E+03

< LLD (0 /34 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 33

< LLD (0 /6 )

SEDIMENT GELI GAMMA ZH-65 40 1.24E+02

< LLD (0 /34 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/KGCDRY))

32 33 33

< LLD (0 /6 )

SEDIMENT GELI GAMMA CD-60 40 6.27E+01 5.16E+02 (14 /34 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/KG(DRY))

( 4.90E+01 - 1.40E+03) 32 33 33 1.06E+03(5 /6 )

( 6.90E+02 - 1.40E+03)

SEDIMENT GELI GAMMA K-40' 40 5.91E+02 5.95E+03 (31 /34 )

9.02E+03(4 /6 )

23 24 25 26 27 (PCI/KG(DRY))

( 2.80E+02 - 1.50E+04)

( 5.00E+03 - 1.20E+04) 32 33 33 1.30E+04(5 /6 )

( 1.20E+04 - 1.50E+04)

SEDIMENT GELI GAMMA BALA-140 40 1.06E+03

< LLD (0 /34 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 33

< LLD (0 /6 )

~~ SEDIMENT GELI GAMMA BE-7 40 5.93E+02 4.64E+02 (5 /34 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/KG(DRY))

( 3.00E+02 - 5.60E+02) 32 33 33 5.60E+02(1 /6 )

( 5.60E+02 - 5.60E+02)

SEDIMENT GELI GAMMA ZR-95 20 1.43E+02

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 33

< LLD (0 /3 )

-112-1

.c a

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH JUNE.1982 THROUGH HOVEMBER,1982 SEMI-AHHUAL

SUMMARY

SAMPLE TYPE ANALYSIL ISOTOPE HUMBER L.L D INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEANCH/ TOTAL)

STATIONS USED 0F RANGE RANGE FOR IHDICA10R MEAN t

ANALYSES PERFORMED STATIDH STATI0H-MEAH(N/ TOTAL)

RANGE i

SEDIMENT GELI GAMMA HB-95 20 1.44E+02

< LLD (O /17 )

< LLD (0 /3 )

23 24 25 P6 27 (PCI/KG(DRY))

32 33 33

< LLD (0 /3 )

SEDIMENT GELI GAMMA 58-125 40 1.21E+02

< LLD (0 /34 )

< LLD (0 /6 )

23 24 25 26 27 i

(PCI/KG(DRY))

32 33 33

< LLD (0 /6 )

1 SEDIMENT GELI GAMMA CE-141 40 1.80E+02

< LLD (0 /34 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 33

< LLD (0 /6 )

SEDIMENT GELI GAMMA RU-103 40 8.52E+01

< LLD (0 /34 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 33

< LLD (O /6 )

SEDIMENT GELI GAMMA CR-51 43 4.64E+02

< LLD (O /34 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 33

< LLD (0 /6 )

(

,I SEDIMENT GELI GAMMA RA-226 40 9.78E+01 3.24E+02 (33 /34 )

2.52E+02(6 /6 3 23 24 25 26 27

]

(PCI/KG(DRY))

( l.30E+02 - 5.30E+02)

( 1.40E+02 - 3.20E+02) 32 33 l

26 4.30E+02(2 /2 )

l

( 3.50E+02 - 5.10E+02) 1 SEDIMENT GELI GAMMA I-131 40 2.16E+02

< LLD (0 /34 )

< LLD (0 /6 3 23 24 25 26 27 (PCI/KG(DRY))

32 33

~

33

< LLD (0 /6 )

-113-1

s -

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH JUNE.1982 THROUGH HOVEMBER,1982 SEMI-ANNUAL

SUMMARY

SAMPLE TYPE AHALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(N/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAH ANALYSES PERFORMED STATION STATIDH-MEAH(H/ TOTAL)

RANGE o

SEDIMENT GELI GAMM4 HP-239 21 1.12E+05

< LLD (0 /18 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 33

< LLD (0 /3 )

SEDIMENT GELI GAMMA RU-106 40 4.02E+02

< LLD (0 /34 )

< LLD (0 /6 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 33

< LLD (0 /6 )

1 SEDIMENT GELI GAMMA C0-57 40 3.90E+01

< LLD (0 /34.)

< LLD (0 /6 3 23 24 25 26 27 (PCI/KG(DRY))

32 33 33

< LLD (0 /6 )

SEDIMENT GELI GAMMA CS-137 40 5.31E+01 1.88E+02 (18 /34 )

4.10E+01(1 /6 )

23 24 25 26 27 (PCI/KG(DRY))

( 2.90E+01 - 6.50E+02)

( 4.10E+01 - 4.10E+01) 32 33 32 2.59E+02(5 /6 )

( 5.90E+01 - 6.50E+02)

SEDIMENT STRONTIUM-89 16 1.22E+01 2.40E+01 (7 /14 3 2.28E+01(1 /2 )

23 24 25 26 27 (PCI/KG(DRY))

( 1.07E+01 - 6.02E+01)

( 2.28E+01 - 2.28E+01) 32 33 26 6.02E+01(1 /2 )

( 6.02E+01 - 6.02E+01) i

"' SEDIMENT STRONTIUM-90 16 6.19E+00

< LLD (0 /14 )

< LLD (0 /2 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 33

< LLD (0 /2 )

l

-114-9

?-

.c s

TABLE 19 RADIOLOGICAL ENVIRONMENTAL MOHITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE 1982 THROUGH AUGUST,1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE AHALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATI0HS USED OF RANGE RANGE FOR INDICATOR MEAH ANALYSES PERFORMED VEGETATION GROSS BETA 15 3.30E+01 2.23E+03 (15 /15 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(WET))

( 1.77E+03 - 2.69E+03)

(

AIR PARTICULATE GROSS ALPHA 52 6.30E-04 1.33E-03 (23 /33 )

1.23E-03(17 /19 )

1 2 3 4 5 (PCI/M3

)

( 5.87E 2.27E-03)

( 3.32E 2.43E-03)

AIR PARTICULATE GROSS BETA 52 5.34E-03 1.53E-02 (29 /33 )

1.47E-02(19 /19 )

1 2 3 4 5 (PCI/M3

)

( 7.32E 2.88E-02)

( 3.59E 2.81E-02)

AIR PARTICULATE STRONTIUM-89 5

1.17E-03

< LLD (0 /3 )

< LLD (0/23 1 2 4 (PCI/M3

)

AIR PARTICULATE STRONTIUM-90 5

9.90E-04

< LLD (0 /3 )

< LLD (0 /2 )

1 2 4 (PCI/M3

)

PRECIPITATIDH GROSS BETA-SS 24 1.41E+00 8.67E-01-(2 /15 )

1.07E+00(2 /9 )

1 2 3 4 5 (PCI/L

)

( 4.05E 1.33E+00)

( 9.73E 1.16E+00)

PRECIPITATIDH GROSS BETA-DS 24 1.70E+00 4.47E+00 (11 /15 )

4.07E+06(9 /9 )

1 2 3 4 5 (PCI/L

)

( 9.95E 9.55E+00)

( 2.44E+00 - 6.82E+00)

PRECIPITATIDH TRITIUM 24 1.46E+02

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION STRONTIUM-89 24 5.29E-01

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION STRONTIUM-90 24 5.98E-01

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

AIR IODINE IODIHE-131 51 3.42E-02

< LLD (0 /33 )

< LLD (0 /18 3 1 2 3 4 5 (PCI/M3

)

SURFACE WATER GROSS ALPHA-SS 24 8.94E-01

< LLD (O /21 )

< LLD (0/31 23 24 25 26 27 (PCI/L

)

32 33

-115-l

~

I e

RADIOLOGICAL ENVIROHMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE 1982 THROUGH AUGUST,1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDMS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED SURFACE WATER GROSS ALPHA-DS 24 2.98E-01 1.27E+00 (20 /21 )

1.81E+00(3 /3 3 23 24 25 26 27 (PCI/L

)

( 4.50E 2.01E+00)

( l.61E+00 - 1.97E+00) 32 33 SURFACE WATER GROSS BETA-SS 24 1.26E+00 9.29E-01 -(1 /21 ).

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

( 9.29E 9.29E-01) 32 33 SURFACE WATER GROSS BETA-DS 24 1.49E+01 1.63E+02 (16 /21 )

2.08E+02(3 /3 )

23 24 25 26 27 (PCI/L

)

( 2.97E+00 - 2.44E+02)

( l.87E+02 - 2.45E+02) 32 33 SURFACE WATER CALCIUM BY AA 24 8.00E-02 1.48E+02 (21 /21 )

2.27E+02(3 /3 )

23 24 25 26 27 (MG/L

)

( l.00E 3.25E+02)

( 1.20E+02 - 3.50E+02) 32 33 SURFACE WATER TRITIUM 24 1.66E+02

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L 32 33 l

t SURFACE WATER IDDINE-131 24 1.38E-01

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 l

(PCI/L

)

32 33 SURFACE WATER RADIUM-226 24 8.73E-02 3.16E-01 (12 /21 )

1.49E-01(1 /3 )

23 24 25 26 27 (PCI/L

)

( 4.53E 6.81E-01)

( l.49E 1.49E-01) 32 33 SURFACE WATER RADIUM-228 24 1.06E+00 5.39E-01 (1 /21 )

< LLD (0/33 23 24 25 26 27 (PCI/L

)

( 5.39E 5.39E-01) 32 33 SURFACE WATER STRONTIUM-89 24 4.66E-01

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER STRONTIUM-90 24 5.56E-01

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER TOTAL URAHIUM 24 1.43E-01 9.71E-01 (20 /21 )

1.41E+00(3 /3 )

23 24 25 26 27 (PCI/L

)

( 2.60E 1.65E+00)

( 1.29E+00 - 1.59E+00) 32 33 WELL WATER GROSS ALPHA-SS 18 5.08E-01 3.34E-01 (1 /18 )

(.

/. )

1 18 19 20 21 (PCI/L

)

( 3.34E 3.34E-01)

(

)

22

-116-

RADIOLOGICAi. ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTEk CREEK HUCLEAR GENERATING STATION JUNE.1982 THROUGH AUGUST.1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE AHALYSIS ISOTOPE HUMBER LLD INDICATOR-NEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED 0F RANGE RANGE FOR INDICATOR NEAN ANALYSES PERFORMED WELL WATER GROSS ALPHA-DS 18 2.13E+00 3.33E+00 (8 /18 )

(,

/. )

1 18 19 20 21

)

22 (PCI/L

)

( l.75E+00 - 4.87E+00)

(

WELL WATER GROSS BETA-SS 18 7.96E-01 6.31E-01 (1 /18 )

(.

/. )

1 18 19 20 21

)

22 (PCI/L

)

( 6.31E 6.31E-01)

(

WELL WATER GROSS BETA-DS 18 1.26E+00 2.15E+00 (12 /18 )

(.

/. )

1 18 19 20 21 4

)

22 (PCI/L

)

( 1.08E+00 - 3.23E+00)

(

WELL WATER POTASSIUM-40 6

8. 6 0 E- 01 1.74E+00 (2 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

( l.43E+00 - 2.05E+00)

(

)

22

(

WELL WATER TRITIUM 6

1.76E+02

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22 WELL WATER RADIUM-226 6

8.38E-02 2.97E-01 (1 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

( 2.97E 2.97E-01)

(

)

22 WELL WATER RADIUM-228 6

6.47E-01

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22 WELL WATER TOTAL URANIUM 6

1.10E-01 3.70E-01 (6 /6 )

C. /. )

1 18 19 20 21 (PCI/L

)

( 2.40E 4.90E-01)

(

)

22 CLAMS GROSS ALPHA 12 5.53E+01 1.16E+02 (6 /9 )

1.01E+02(3 /3 )

23 24 25

__ (PCI/KG(WET))

( 7.66E+01 - 1.39E+02)

( 8.29E+01 - 1.38E+02)

~l CLAMS GROSS PETA 12 2.39E+01 8.73E+02 (9 /9 )

8.28E+02(3 /3 )

23 24 25 (PCI/KG(WET))

( 1.95E+02 - 1.39E+03)

( 8.01E+02 - 8.49E+02)

CLANS CALCIUM BY AA 4

8.00E-02 4.08E+01 (3 /3 )

4.50E+01(1 /1 )

23 24 25 i

(MG/GM(WET) )

( 3.00E+01 - 5.00E+01)

( 4.50E+01 - 4.50E+01)

CLAMS STRONTIUM-89 4

6.07E+00

< LLD (0 /3 )

< LLD

( 0 /1 )

23 24 25 (PCI/KG(WET))

-117-I

RADIOLOGICAL ENVIRONMENTAL MOHITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATI0H JUNE 1982 THROUGH AUGUST 1982 FIRST GUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAH AHALYSES PERFORMED CLAMS STRONTIUM-90 4

4.12E+00

< LLD (0 /3 )

< LLD

( 0 /1 )

23 24 25 (PCI/KG(WET))

SOIL GROSS BETA 15 1.65E+03 4.41E+03 (14 /15 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

( 1.90E+03 - 9.llE+03)

(

PASTURE GROSS BETA 3

6.05E+01 3.85E+03 (3 /3 )

(.

/. )

28. 29 30

)

(PCI/KG(WET))

( 3.15E+03 - 4.53E+03)

(

PASTURE CALCIUM BY AA 3

8.00E-02 5.33E+01 (3 /3 )

(.

/. )

28 29 30 (MG/GM(WET) )

( 4.00E+01 - 6.00E+.01)

(

)

PASTURE STRONTIUM-8s 3

1.84E+01

< LLD (0 /3 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

PASTURE STRONTIUM-90 3

1.93E+02

< LLD (0 /3 )

(,

/. )

28 29 30

)

(PCI/KG(WET))

(

SEDIMENT GROSS ALPHA 8

3.93E+03 7.05E+03 (5 /7 )

< LLD

( 0 /1 )

23 24 25 26 27 (PCI/KG(DRY))

( 4.70E+03 - 1.29E+04) 32 33 SEDIMENT GROSS BETA 8

1.11E+03 8.12E+03 (7 /7 )

1.15E+04(1 /1 )

23 24 25 26 27 (PCI/KG(DRY))

( 1.63E+03 - 1.88E+04)

( 1.13E+04 - 1.13E+04) 32 33 SEDIMENT STRDHTIUM-89 8

8.73E+00

< LLD (0/73

< LLD

( 0 /1 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 SEDIMENT STRONTIUM-90 8

8.99E+00

< LLD (0 /7 )

< LLD

( 0 /1 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 AIR PARTICULATE GELI GAMMA CE-144 52 3.68E-02

< LLD (0 /33 )

< LLD (0 /19 )

1 2 '3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA AG-110M 52 5.39E-03

< LLD (0 /33 )

< LLD (0 /19 )

1 2 3 4 5 l

(PCI/M3

)

l

-118-

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH JUNE.1982 THROUGH AUGUST,1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAff ANALYSES PERFORMED AIR PARTICULATE GELI GAMMA TE-129M 52 2.41E-01

< LLD (0 /33 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

j i

AIR PARTICULATE GELI GAMMA MD-99 41 4.86E-01

< LLD (0 /26 )

< LLD (0 /15 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA ZRNO-95 52 6.38E-03

< LLD (0 /33 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE CELI GAMMA CS-134 52 4.88E-03

< LLD (0 /33 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA CO-58 52 6.05E-03

< LLD (0 /33 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA MH-54 52 5.52E-03

< LLD (0 #33 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA TH-232 52 1.89E-02

< LLD (0 /33 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA FE-59 52 1.37E-02

< LLD (0 /33 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

i AIR PARTICULATE GELI GAMMA CS-136 52 1.41E-02

< LLD (O /33 )

__ (PCI/M3

)

< LLD (0 /19 )

1 2 3 4 5 AIR PARTICULATE GELI GAMMA ZH-65 52 1.18E-02

< LLD (9 /33 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA CD-60 52 7.36E-03

< LLD (0 /33 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA K-40 52 9.20E-02

< LLD (0 /33 3 1.01E-01(2 /19 )

1 2 3 4 5 (PCI/M3

)

( 8.30E 1.20E-01)

-119-I

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH JUNE.1982 THROUGH AUGUST.1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED AIR PARTICULATE GELI GAMMA BALA-140 52 1.77E-02

< LLD (0 /33 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA BE-7 52 6.88E-02 1.10E-01 (14 /33 )

8.59E-02(11 /19 )

1 2 3 4 5 (PCI/M3,

)

( 6.20E 1.50E-01)

( 2.80E 1.50E-01)

AIR PARTICULATE GELI GAMMA SB-125 52 1.49E-02

< LLD (0 /33 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/N3

)

AIR PARTICULATE GELI GAMMA CE-141 51 1.23E-02

< LLD (0 /32 )

< LLD

( 0 /19 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA RU-103 52 7.09E-03

< LLD (0 /33 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3 3.

AIR PARTICULATE GELI GAMMA CR-51 52 6.89E-02

< LLD (0 /33 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA RA-226 52 1.19E-02

< LLD (0 /33 3

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA I-131 51 2.84E-02

< LLD (O /32 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA HP-239 19 7.70E+01

< LLD (0 /11 )

< LLD (0 /8 )

1 2 3 4 5

_ (PCI/M3

)

AIR PARTICULATE GELI GAMMA RU-106 52 4.71E-02

< LLD (0 /33 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA CO-57 52 4.38E-03

< LLD (0 /33 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA CS-137 52 5.5?E-03

< LLD (0 /33 3

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

-120-l

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH JUNE.1982 THROUGH AUGUST,1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUM 0ER LLD INDICATOR-MEAHfH/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDMS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED PRECIPITATION GELI GAMMA CE-144 8

8.34E+01

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

PRECIPITATIDH GELI GAMMA AG-110M 8

9.15E+00

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

PRECIPITATIDH GELI GAMMA TE-129M 8

3.96E+02

< LLD (0 /5 )

< LLD (0/33 1 2 3 4 5 (PCI/L

)

PRECIPITATION GELI GAMMA MD-99 8

5.24E+02

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

PRECIPITATIDH GELI GAMMA CS-134 8

8.72E+00

< LLD (0 /5 )

< LLD (0/33 1 2 3 4 5 (PCI/L

)

PRECIPITATIDH GELI GAMMA CO-58 8

9.89E+00

, < LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

PRECIPITATIDH GELI GAMMA MM-54 8

8.76E+00

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION GELI GAMMA TH-232 8

2.99E+01

< LLD (0 /5 )

< LLD (0/31 1 2 3 4 5 (PCI/L

)

PRECIPITATION GELI GAMMA FE-59 8

1.85E+01

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L 1

PRECIPITATION GELI GAMMA CS-136 8

1.89E+01

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION GELI GAMMA ZH-65 8

1.69E+01

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

PRECIPITATIDH GELI GAMMA CD-60 8

7.89E+00

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

-121-l

RADIOLOGICAL ENVIRONMENTAL MOHITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE 1982 THROUGH AUGUST.1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/TDTAL)

STATIONS USED OF RANGE RANGE FOR INDICAIOR NEAH ANALYSES PERFORMED

/

PRECIPITATION GELI GAMMA K-40 8

6.90E+01

< LLD (0 /5 )

< LLD (0 /3 3 1 2 3 4 5 (PCI/L

)

PRECIPITATIDH GELI GAMMA B AL A-140 - 8 1.67E+01

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

PRECIPITATIDH GELI GAMMA BE-7 8

9.92E+01

< LLD (0 /5 )

< LLD (C /3 )

1 2 3 4 5 (PCI/L

)

PRECIPITATIDH GELI GAMMA ZR-95 8

1.85E+01

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION GELI GAMMA HB-95 8

1.17E+01

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

PRECIPITATIDH GELI GAMMA SB-125 8

2.91E+01

< LLD (0 /5 )

< LLD (0/33 1 2 3 4 5 (PCI/L

)

PRECIPITATION GELI GAMMA CE-141 8

2.41E+01

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION GELI GAMMA RU-103 8

1.25E+01

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

PRECIPITATIDH GELI GAMMA CR-51 8

1.22E+02

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION GELI GAMMA RA-226 8

1.82E+01

< LLD (0 /5 )

< LLD (0/33 1 2 3 4 5 (PCI/L

)

PRECIPITATION GELI GAMMA I-131 8

3.81E+01

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION GELI GAMMA HP-239 6

1.67E+05

< LLD (0 /5 )

< (LD (0 /1 3 1 2 3 4 5 (PCI/L

)

-122-1

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM EUMMARY OYSTER CREEK HUCLEAR GENERATING STATION JUNE.1982 THROUGH AUGUST.1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUM 0ER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED PRECIPITATION GELI GAMMA RU-106 8

9.02E+01

< LLD (0 /5 )

< LLD (0/33 1 2 3 4 5 (PCI/L 3

PRECIPITATION GELI GAMMA CD-57 8

1.09E+01

< LLD (0 /5 )

< LLD (0/33 1 2 3 4 5 (PCI/L

)

PRECIPITATION GELI GAMMA CS-137 8

9.37E+00

< LLD (0 /5 )

< LLD (0 /3 )

1 2 3 4 5 (PCI/L

)

PRECIPITATIDH HAI GAMMA CE-144 16 5.85E+01

< LLD (0 /10 )

< LLD (O /6 3 1 2 3 4 5 (PCI/L

)

j PRECIPITATION HAI GAMMA AG-110M 16 5.26E+00

< LLD (0 /10 )

< LLD (0 /6 )

1 2 3 4 5 (PCI/L

)

PRECIPITATIDH HAI GAMMA TE-129M 16 1.14E+02

< LLD (0 /10 )

< LLD (O /6 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION HAI GAMMA MD-99 16 2.36E+03

< LLD (0 /10 )

< LLD (0 /6 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION HAI GAMMA ZRH0-95 16 5.76E+00

< LLD (0 /10 )

< LLD (0 /6 )

I 2 3 4 5 (PCI/L

)

PRECIPITATIDH HAI GAMMA CS-134 16 5.01E+00

< LLD (0 /10 )

< LLD (0 /6 )

1 2 3 4 5

__ (PCI/L

)

PRECIPITATION HAI GAMMA CD-58 16 5.68E+00

< LLD (0 /10 )

< LLD (O /6 )

1 2 3 4 5 (PCI/L

)

PRECIPITATIDH HAI GAMMA MH-54 16 5.04E+00

< LLD (O /10 )

< LLD (0 /6 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION HAI GAMMA TH-232 16 2.15E+01

< LLD (0 /10 )

< LLD (0 /6 )

1 2 3 4 5 (PCJ/L

)

-123-

~

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH JUNE.1982 THROUGH AUGUST,1982 FIRST QUARTER SUMt1ARY SAMPLE TYPE ANALYSIS ISOTDPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAN(N/ TOTAL)

STATIONS USED OF RANGE RANGE-FOR INDICATOR MEAH ANALYSES PERFORMED PRECIPITATIDH HAI GAMMA FE-59 16 1.21E+01

< LLD (0 /10 )

< LLD (0 /6 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION HAI GAMMA CS-136 16 1.60E+01

< LLD (0 /10 )

< LLD (0 /6 )

1 2 3 4 5 (PCI/L

)

f PRECIPITATION HAI GAMMA TE-132 16 2.24E+02

< LLD (0 /10 )

< LLD (0 /6 )

1 2 3 4 5 (PCI/L

)

PRECIPITATIDH HAI GAMMA ZH-65 16 1.09E+01

< LLD (0 /10 )

< LLD (0 /6 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION HAI GAMMA CO-60 16 5.47E+00

< LLD (0 /10 )

< LLD (0 /6 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION HAI GAMMA K-40 16 5.93E+01

< LLD (0 /10 )

< LLD (0/63 1 2 3 4 5 (PCI/L

)

PRECIPITATIDH HAI GAMMA BALA-140 16 1.34E+01

< LLD (O /10 )

< LLD (0 /6 )

1 2 3 4 5 (PC1/L

)

PRECIPITATIDH HAI GAMMA BE-7 16 6.08E+01

< LLD (0 /10 )

< LLD (0 /6 )

1 2 3 4 5 (PCI/L

)

PRECIPITATIDH HAI GAMMA CR-51 16 7.29E+01

< LLD (0 /10 )

< LLD (0 /6 )

1 2 3 4 5

__ (PCI/L

)

PRECIPITATION HAI GAMMA RA-226 16 1.01E+01

< LLD (0 /10 )

< LLD (0 /6 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION HAI GAMMA I-131 16 2.55E+01

< LLD (0 /10 )

< LLD (0 /6 )

1 2 3 4 5 (PCI/L

)

PRECIPITATIDH HAI GAMMA HA-22 16 5.40E+00

< LLD (0 /10 )

< LLD (0 /6 )

1 2 3 4 5 (PCI/L

)

-124-1

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE,1982 THROUGH AUGUST.1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(N/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED PRECIPITATIDH HAI GAMMA RU-106 16 5.09E+01

< LLD (0 /10 )

< LLD (0 /6 )

1 2 3 4 5 (PCI/L

)

i PRECIPITATION HAI GAMMA I-133 16 6.15E+00

< LLD (0 /10 )

< LLD (0 /6 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION HAI GAMMA CS-137 16 5.94E+00

< LLD (0 /10 )

< LLD (0 /6 3 1 2 3 4 5 (PCI/L

)

CABBAGE HAI GAMMA CE-144 2

4.85E+01

< LLD (0 /1 )

1 (PCI/KG(WET))

CABBAGE HAI CAMMA AG-110M 2

1.20E+01

< LLD (0 /1 )

1 i

(PCI/KG(WET))

COBBAGE HAI GAMMA TE-129M 2

2.20E+02

< LLD (0 /1 )

< LLD (0/13 1

(PCI/KG(WET))

a

(

CABBAGE HAI GAMMA MD-99 2

5.35E+03

< LLD (0 /1 )

1 (PCI/KG(WET))

CABBAGE HAI GAMMA ZRHB-95 2

1.40E+01

< LLD (0 /1 )

1 (PCI/KG(WET))

CABBAGE HAI GAMMA CS-134 2

1.25E+01

< LLD (0 /1 )

1 (PCI/KG(WET))

CABBAGE HAI GAMMA CD-58 2

1.35E+01

< LLD

( 0 /1 )

< LLD

( 0 /1 3 1

(PCI/KG(WET))

CABBAGE NAI GAMMA MN-54 2

1.30E+01

< LLD (0 /1 )

< LLD

( 0 /1 )

1 (PCI/KG(WET))

CABBAGE HAI GAMMA TH-232 2

4.70E+01

< LLD (0 /1 )

1 (PCI/KG(WET))

-125-1

m RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH JUNE.1932 THROUGH AUGUST,1982 FIRST QUARTER SUMr1ARY SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAN(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATI0HS USED OF RANGE RANGE FOR INDICATOR MEAN AHALYSES PERFORMED CABBAGE HAI GAMMA FE-59 2

3.00E+01

< LLD (0 /1 )

< LLD

( 0 /1 )

1 (PCI/KG(WET))

CABBAGE HAI GAhMA CS-136 2

3.65E+01

< LLD (G /1 )

< LLD (O /1 3 1

(PCI/KG(WET))

CABBAGE HAI GAMMA TE-132 2

2.55E+02

< LLD (0 /1 )

1 (PCI/KG(WET))

CABBAGE HAI GAMMA ZH-65 2

3.25E+01

< LLD (0 /1 )

< LLD (0 /1 3 1

(PCI/KG(WET))

CABBAGE HAI GAMMA CO-60 2

1.25E+01

< LLD (0 /1 )

< LLD

( 0 /1 )

1 (PCI/KG(WET))

CAB 9 AGE HAI GAMMA K-40 2

3.10E+02 1.80E+03 (1 /1 )

2.50E+03(1 /1 1 1

(PCI/KG(WET))

( 1.80E+03 - 1.80E+03)

( 2.50E+03 - 2.50E+03)

CABBAGE HAI GAMMA BALA-140 2 2.85E+01

< LLD (0 /1 )

1 (PCI/KG(WET))

CABBAGE HAI GAMMA BE-7 2

1.15E+02

< LLD (0 /1 )

1 (PCI/KG(WET))

CABBAGE HAI GAMMA CR-51 2

1.15E+02

< LLD (0 /1 )

< LLD (O/13 1

(PCI/KG(NET))

CABBAGE HAI GAMi1A RA-226 2

2.35E+01

< LLD (0 /1 )

< LLD (0/11 1

(PCI/KG(WET))

CABBAGE HAI GAMMA I-131 2

4.10E+01

< LLD (0 /1 )

< LLD (0 /1 3 1

(PCI/KG(NET))

CABBAGE HAI GAMMA HA-22 2

1.35E+01

< LLD (O /1 )

< LLD (0/13 1

(PCI/KG(WET))

-126-i 4

-.__-y..

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH JUNE 1982 THROUGH AUGUST,1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED CABBAGE HAI GAMMA RU-106 2

1.13E+02

< LLD (0 /1 )

1 (PCI/KGCWET))

CABBAGE HAI GAMMA I-133 2

1.25E+01

< LLD (0 /1 )

1 (PCI/KG(WET))

CABBAGE HAI GAMMA CS-137 2

1.25E+01

< LLD (0 /1 )

< LLD

( 0 /1 )

1 (PCI/KG(WET))

CORN HAI GAMMA CE-144 5

9.62E+01

< LLD (0 /4.)

< LLD (0 /1 )

1 2 3 4 (PCI/KG(WET))

/

CORH HAI GAMMA AG-110M 5

1.92E+01

< LLD (0 /4')

< LLD (0 /1 )

1 2 3 4 (PCI/KG(WET))

I CORH HAI GAMMA TE-129M 5

4.20E+02

< LLD (0 /4 )

< LLD

( 0 /1 )

1 2 3 4 (PCI/KG(WET))

i CORH HAI GAMMA MO-99 5

6.12E+03

< LLD (0 /4 )

< LLD (0 /1 )

1 2 3 4 (PCI/KG(WET))

CORN.

HAI GAMMA ZRHB-95 5

2.54E+01

< LLD (0 /4 )

< LLD (0 /1 )

1 2 3 4 (PCI/KG(WET))

CORH HAI GAMMA CS-134 5

1.90E401

< LLD (0 /4 )

< LLD (0 /1 )

1 2 3 4 (PCI/KG(WET))

CORH HAI GAMMA CD-58 5

2.16E+01

< LLD (0 /4 )

< LLD (0 /1 )

1 2 3 4 (PCI/KG(HET))

CORH HAI GAMMA MH-54 5

2.24E*01

< LLD (0 /4 )

< LLD (0 /1 )

1 2 3 4

__ (PCI/KG(WET))

CORN HAI GAMMA TH-232 5

8.38E+01

< LLD (0 /4 )

< LLD

( 0 /1 )

1 2 3 4 (PCI/KG(WET))

-127-

a-RADIOLOGICAL ENVIROHMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATIHG STATIDH JUNE.1982 THROUGH AUGUST.1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAH ANALYSES PERFORMED 4'

CORN HAI GAMMA FE-59 5

5.90E+01

< LLD (0 /4 3

< LLD

( 0 /1 )

1 2 3 4 (PCI/KG(WET))

CORH HAI GAMMA CS-136 5

6.88E+01

< LLD (0 /4 )

< LLD

( 0 /1 )

1 2 3 4 (PCI/KG(WET))

CORN HAI GAMMA TE-132 5

3.78E+02

< LLD (0 /4 )

< LLD (0 /1 )

1 2 3 4 (PCI/KG(WET))

CORN NAI GAMMA ZH-65 5

5.86E+01

< LLD (0 /4 )

< LLD (0 /1 3 1 2 3 4 (PCI/KG(WET))

CORH HAI GAMMA CD-60 5

2.50E+01

< LLD (0 /4 )

< LLD (0 /1 )

1 2 3 4 (PCI/KG(WET))

CO2N HAI GAMMA K-40 5

4.70E+0?

2.90E+03 (4 /4 )

3.30E+03(1 /1 )

1 2 3 4 (PCI/KG(WET))

( 2.40E+03 - 3.4GE+03)

( 3.30E+03 - 3.30E+03)

CORN HAI GAMMA BALA-140 5 6.28E+01

< LLD (0 /4 )

< LLD (0 /1 )

1 2 3 4 (PCI/KG(WET))

CORH HAI GAMMA BE-7 5

1.88E+02

< LLD (0 /4 )

< LLD (0 /1 )

1 2 3 4 (PCI/KG(WET))

CORN HAI GAMMA CR-51 5

2.10E+02

< LLD (0 /4 )

< LLD (0 /1 3 1 2 3 4

__ (PCI/KG(WET))

f CORN HAI GAMMA RA-226 5

3.74E+01

< LLD (0 /4 )

< LLD

( 0 /1 )

1 2 3 4 (PCI/KG(WET))

CORN HAI GAMMA I-131 5

5.62E+01

< LLD (0 /4 )

< LLD (0 /1 1 1 2 3 4 (PCI/KG(WET))

CORH HAI GAMMA HA-22 5

2.50E+01

< LLD (0 /4 )

< LLD (0 /1 )

1 2 3 4 (PCI/KG(WET))

-128-t

x.

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH JUNE.1982 THROUGH AUGUST 1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAN(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICAIOR MEAN ANALYSES PERFORNED CORH HAI GAMMA RU-106 5

1.92E+02

< LLD (0 /4 )

< LLD (0 /1 )

1 2 3 4 (PCI/KG(WET))

CORN HAI GAMMA I-133 5

2.50E+01

< LLD (0 /4 )

< LLD

( 0 /1 )

1 2 3 4 (PCI/KG(WET))

CORN HAI GAMMA CS-137 5

2.20E+01

< LLD (0 /4 )

< LLD

( 0 /1 )

1 2 3 4 (PCI/KG(WET))

CUCUNDERS HAI GAMMA CE-144 1

1.60E+01

< LLD (0 /1 )

C. /. )

5 (PCI/KG(WET))

(

)

CUCUMBERS HAI GAMMA AG-110M 1

6.50E+00

< LLD (0 /1 )

(.

/. )

5

)

(PCI/KG(WET))

(

CUCUMBERS HAI GAMMA TE-129M 1-

.1.30E+02

< LLD (0/1)

(.

/. )

5 (PCI/KG(WET))-

(

)

CUCUMBERS HAI GAMMA MO-99 1

2.40E+03

< LLD (O /1 )

(.

/. )

5 (PCI/KG(WET))

(

)

CUCUMBERS HAI GAMMA ZRHB-95 1

7.30E+00

< LLD (O/1)

(.

/. 1 5

(PCI/KG(WET))

(

)

CUCUMBERS HAI GAMMA CS-134 1

6.30E*00

< LLD (0 /1 )

C. /. )

5 (PCI/KG(WET))

(

)

CUCUMBERS HAI GAMMA CO-58 1

7.20E+00

< LLD (0 /1 )

(.

/. )

5 (PCI/KG(WET))

(

)

CUCUi1BERS HAI GAMMA MH-54 1

6.40E+00

< LLD (0 /1 )

(.

/. )

5 (PCI/KG(WET))

(

)

CUCUMBERS HAI GAMMA TH-232 1

3.10E+01

< LLD (0 /1 )

(. /. )

5 (PCI/KG(WET))

(

3

-129-l

x.

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE.1982 THROUGH AUGUST,1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDIC% TOR MEAN ANALYSES PERFORMED CUCUNBERS HAI GAMMA FE-59 1

1.80E+01

< LLD (O /1 )

C. /. )

5

)

(PCI/KG(WET))

(

CUCUMBERS HAI GAMMA CS-136 1

2.20E+01

< LLD (0 /1 )

C. /. )

5 (PCI/KG(WET))

(

)

CUCUMBERS HAI GAMMA TE-132 1

9. ODE +01

< LLD (O /1 )

(.

/. )

5

)

(PCI/KG(WET))

(

CUCUMBERS HAI GAMMA ZH-65 1

1.60E+01

< LLD (O /1 )

(.

/. )

5 (PCI/KG(WET))

(

)

CUCUMBERS NAI GAMMA CD-60 1

6.20E+00

< LLD (O /1 )

(.

/. )

5 (PCI/KG(WET))

(

)

i CUCUMBERS HAI GAMMA K-40 1

1.60E+02 1.40E403 (1 /1 )

(.

/. )

5 (PCI/KG(WET))

( l.40E+03 - 1.40E+03)

(

)

CUCUMBERS HAI GAMMA BALA-140 1 1.50E+01

< LLD (0 /1 )

C. /. )

5 (PCI/KG(WET))

(

)

CUCUMBERS HAI GAMMA BE-7 1

5.70E+01

< LLD (O /1 )

(.

/. )

5 (PCI/KG(WET))

(

)

CUCUMBERS HAI GAMMA CR-51 1

4.60E+01

< LLD (0 /1 )

(, /. )

5 1

(PCI/KG(WET))

(

)

CUCUMBERS HAI GAMMA RA-226 1

1.10E+01

< LLD (O /1 )

(, /. )

5 (PCI/KG(WET))

(

3 CUCUMBERS NAI GAMMA I-131 1

1.80E+01

< LLD (O /1 )

(.

/. )

5 (PCI/KG(WET))

(

)

CUCUMBERS HAI GAMMA HA-22 1

6.30E*00

< LLD (0 /1 )

(,

/. )

5 (PCI/KG(NET))

3

-130-1 1

. --c RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE.1982 THROUGH AUGUST.1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAHtH/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAH ANALYSES PERFORMED CUCUMBERS HAI GAMMA RU-106 1

6.40E+01

< LLD (0 /1 )

(.

/. )

5 I

(PCI/KG(WET))

('

CUCUMBERS HAI GAMMA I-133 1

6.20E+00

< LLD (0 /1 )

(,

/. )

5 3

(PCI/KG(WET))

(

CUCUMBERS HAI GAMMA CS-137 1

6.20E+00

< LLD (0 /1 )

C. /. )

5

)

~(PCI/KG(WET))

(

/

SURFACE WATER NAI GAMMA CE-144 24 6.30E+01

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA AG-110M 24 6.08E+00

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA TE-129M 24 1.18E402

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA M0-99 24 8.38E+02

< LLD (0 /21 )

< LLD (O /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA ZRHB-95 24 6.52E+00

< LLD (0 /21 )

< LLD (0/33 23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA CS-134 24 5.97E+00

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA CO-58 24 6.55E+00

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA MH-54 24 6.05E+00

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L 3

32 33 SURFACE WATER HAI GAMMA TH-232 24 2.29E+01

< LLD (0 /21 )

< LLD (O /3 )

23 24 25 26 27 (PCI/L

)

32 33

-131-l

v.--.

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

i OYSTER CREEK HUCLEAR GENERATING STATION JUNE.1982 THROUGH AUGUST.1982 FIRST QUARTER

SUMMARY

i SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAN(H/ TOTAL)

BACKROUND-MEAH(N/ TOTAL)

STATIDHS USED 0F RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED l

SURFACE WATER HAI GAMMA FE-59 24 1.31E+01

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA CS-136 24 1.43E+61

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA TE-132 24 1.84E+02

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33

$URFACE WATER HAI GAMMA ZH-65 24 1.29E+01

< LLD (0 /21 )

< LLD (0/33 23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA CD-60 24 6.22E+00

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATr>

HAI GAMMA K-40 24 9.02E+01 2.26E+02 (15 /21 )

3.30E+02(3 /3 )

23 24 25 26 27 (PCI/L

( 1.10E+02 - 3.30E+02)

( 2.30E+02 - 3.90E+02) 32 33 SURFACE WATER HAI GAMMA BALA-140 24 1.20E*01

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA BE-7 24 6.57E+01

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA CR-51 24 7.66E+01

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27

__ (PCI/L

)

32 33 SURFACE WATER HAI GAMMA RA-226 24 1.14E+01

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA I-131 24 2.06E+01

< LLD (0 /21 )

< LLD (0 /3 )

23 24 f:S 76 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA HA-22 24 6.35E+00

< LLD (0 /21 3

< LLD (0 /3 )

23 24 25 26 27 r

(PCI/L

)

32 33

-132-l

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK NUCLEAR GENERATING STATION JUNE.1982 THROUGH AUGUST.1982 FIRST QUARTER

SUMMARY

S AMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED SURFACE WATER HAI GAMMA RU-106 24 5.97E+01

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA I-133 24 7.01E+00

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 l

SURFACE WATER HAI GAMMA CS-137 24 6.35E+00

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 i

j GREEN BEANS MAI GAMMA CE-144 2

6.50E+01 C. /. 3

< LLD (0 /2 )

)

i (PCI/KG(WET))

(

GREEN BEANS HAI GAMMA AG-110M 2

1.55E+01

(.

/. )

< LLD (0 /2 )

)

(PCI/KG(WET))

(

GREEN BEANS HAI GAMMA TE-129M 2

3.35E+02 C. /. )

< LLD (0 /2 )

(PCI/KG(kF:T))

(

)

GREEN BEANS HAI GAMMA MD-99 2

8.65E+03 C. /. )

< LLD (0 /2 )

(PCI/KG(WET))

(

)

GREEN BEANS HAI GAMMA ZRHB-95 2

1.80E+01

(. /. )

< LLD (0 /2 )

(PCI/KG(WET))

(

)

GREEN BEANS HAI GAMMA CS-134 2

1.50E+01

(.

/. )

< LLD (0 /2 )

(PCI/KG(WET))

(

)

GREEN BEANS HAI GAMMA CO-58 2

1.75E+01

(,

/. )

< LLD (0 /2 )

(PCI/KG(WET))

(

)

GREEH BEANS HAI GAMMA MH-54 2

1.60E+01

(.

/. )

< LLD (0 /2 )

(PCI/KG(WET))

(

)

GREEN BEANS HAI GAMMA TH-232 2

7.00E+01

(.

/. )

< LLD (0 /2 )

(PCI/KG(WET))

(

)

-133-p a

- _ _ =

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION I

JUNE.1982 THROUGH AUGUST,1982 FIRST QUARTER SUNNARY 3

SAMPLE TYPE ANALYSIS ISOTOPE HUMOER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDMS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED GCEEH BEANS HAI GAMMA FE-59 2

4.05E+01

(.

/. )

< LLD (0 /2 )

)

(PCI/KG(WET))

(

GREEN BEANS HAI GAMMA CS-136 2

5.95E+01

(.

/. )

< LLD (0 /2 J

)

(PCI/KG(WET))

(

GREEH BEANS HAI GAMMA TE-132 2

4.60E+02

(.

/. )

< LLD (0 /2 )

)

(PCI/KG(WET))

(

GREEN BEANS HAI GAMMA ZH-65 2

4.10E+01

(.

/. )

< LLD (0 /2 )

)

(PCI/KG(WET))

(

GREEN BEANS HAI GAMMA CO-60 2

1.60E+01

(.

/. )

< LLD (0 /2 )

)

(PCI/KG(WET))

(

a GREEN BEAHS HAI GAMMA K-40 2

3.10E+02

(.

/. )

1.80E+03(2 /2 )

)

( 1.70E+03 - 1.90E+03)

(PCI/KG(WET))

(

GREEN BEANS HAI GAMMA BALA-140 2 4.00E+01

(.

/. )

< LLD (0 /2 )

)

(PCI/KG(WET))

(

GREEH BEANS HAI GAMMA BE-7 2

1.70E402 C. /. )

< LLD (0 /2 )

(PCI/KG(WET))

(

)

GREEN BEANS HAI GAMMA CR-51 2

1.70E+02

(.

/. )

< LLD (0 /2 )

(PCI/KG(WET))

(

)

3 GREEN BEANS HAI GAMMA RA-226 2

3.10E+01

(.

/. )

< LLD (0 /2 )

(PCI/KGtWET))

(

)

GREEN BEANS HAI GAMMA I-131 2

6.30E+01

(,

/. )

< LLD (0 /2 )

(PCI/KG(WET))

(

3 GREEN BEANS MAI GAMMA HA-22 2

1.60E+01

(,

/. )

< LLD (0 /2 )

(PCI/KG(WET))

(

}

-134-1

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE.1982 THROUGH AUGUST.1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATI0HS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED GREEN BEANS HAI GAMMA RU-106 2

1.50E+02

(.

/. )

< LLD (0 /2 )

(PCI/KG(WET))

(

)

GREEH BEANS HAI GAMMA I-133 2

1.60E+01 C. /. )

< LLD (0 /2 )

)

(PCI/KG(WET))

(

GREEN BEANS HAI GAMMA CS-137 2

1.60E+01

(.

/. )

< LLD (0 /2 )

3 (PCI/KG(WET))

(

TOMATOES HAI GAMMA CE-144 6

2.42E+01

< LLD (O /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

TOMATOES HAI GAMMA AG-110M 6

8.97E+00

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

TOMATOES HAI GAMMA TE-129M 6

1.68E+02

< LLD (0 /4 )

< LLD (0 /2 3 2 3 4 5 (PCI/KG(WET))

TOMATOES HAI GAMMA MO-99 6

3.10E+03

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

TONATOES HAI GAMMA ZRHB-95 6

1.04E+01

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

TOMATOES NAI GAMMA CS-134 6

9.23E+00

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5

__ (PCI/KG(WET))

TOMATOES NAI GAMMA CO-58 6

1.05E+01

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

TOMATOES HAI GAMMA MH-54 6

9.35E+00

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

3 TOMATOES HAI GAMMA TH-232 6

3.88E+01

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

-135-l

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH JUNE 1982 THROUGH AUGUST,1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE NUMBER LLD INDICATOR-MEANCH/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOReMEAH ANALYSES PERFORMED TOMATOES HAI GAMMA FE-59 6

2.32E+01

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

TDMATOES HAI GAMMA CS-136 6

2.73E+01

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

TOMATOES HAI GAMMA TE-132 6

1.51E+02

< LLD (0 /4 )

< LLD (0 /2 ) ~

2 3 4 5'

(PCI/KG(WET))

TOMATOES HAI GAMMA ZH-65 6

2.42E+01

< LLD (O /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

TDMATOES NAI GAMMA CD-60 6

9.45E+00

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

TDMATOES HAI GAMMA K-40 6

2.10E+02 2.02E+03 (4 /4 )

2.15E*03(2 /2 )

2 3 4 5 (PCI/KG(WET))

( 1.80E+03 - 2.40E+03)

( 1.80E+03 - 2.50E+03)

TOMATOES HAI GAMMA BALA-140 6 2.15E+01

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

TOMATOES HAI GAMMA RE-7 6

8.45E+01

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

TOMATOES HAI GAMMA CR-51 6

7.93E+01

< LLD (0 /4 3

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

TDMATOES HAI GAMMA RA-226 6

1.62E+01

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

TOMATOES HAI GAMMA I-131 6

2.72E+01

< LLD (0 /4 )

< LLD (0 /2 3 2 3 4 5

__ (PCI/KG(NET))

TDMATOES HAI GAMMA HA-22 6

1.05E+01

< LLD (0 /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KGtWET))

-136-a

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE.1982 THROUGH AUGUST 1982-FIRST QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(N/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED 1

TOMATOES HAI GAMMA RU-106 6

8.30E+01

< LLD (0 /4 )

< LLD (0/23 2 3 4 5 (PCI/KGtWET))

TOMATOES HAI GAMMA I-133 6

9.15E+00

< LLD (O /4 )

< LLD (0 /2 )

2 3 4 5 (PCI/KG(WET))

TOMATOES NAI GAMMA CS-137 6

9.70E+00

< LLD (0 /4 )

< LLD (0 /2 3 2 3 4 5 (PCI/KG(WET))

O WELL WATER HAI GAMMA CE-144 6

5.57E+01

< LLD (0 /6 )

(. /. )

1 18 19 20 21

)

22 (PCI/L

)

(

WELL WATER HAI GAMMA AG-130M 6

6.40E+00

< LLD (0 /6 )

C. /. )

1 18 19 20 21 (PCI/L

)

(

)

22 WELL WATER HAI GAMMA TE-129M 6

1.22E+02

< LLD (0 /6 )

C. /. )

1 18 19 20 21

)

22 (PCI/L

)

(

I WELL WATER HAI GAMMA MO-99 6

4.25E+02

< LLD (0 /6 )

(,

/. )

1 18 19 20 21 (PCI/L

)

(

)

22 WELL WATER HAI GAMMA ZRHB-95 6

6.55E+00

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22 WELL WATER HAI GAMMA CS-134 6

6.03E+00

< LLD (0 /6 )

(,

/. )

1 18 19 20 21

__ (PCI/L

)

(

)

22 WELL WATER HAI GAMMA C0-58 6

6.53E+00

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22 4

WELL WATER NAI GAMMA MH-54 6

6.05E+00

< LLD (0 /6 )

(.

/. )

1 18 19 20 21

__ (PCI/L 3

(

)

22 WELL WATER HAI GAMMA TH *.I2 6

2.10E+01

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22

-137-I

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SUPMARY OYSTER CREEK HUCLEAR GENERATING STATION JUNE,1982 THROUGH AUGUST.1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAN(H/ TOTAL)

SACKROUND-MEAN(M/ TOTAL)

STATIONS USED l

OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED WELL WATER HAI GAMMA FE-59 6

1.28E+01

< LLD (0 /6 )

(.

/, )

1 18 19 20 21

)

22 (PCI/L

}

(

WELL WATER HAI GAMMA CS-136 6

1.20E+01

< LLD (0 /6 )

(. /. )

1 18 19 20 21

)

22 (PCI/L

)

(

WELL WATER HAI GAMMA TE-132 6

5.22E+01

< LLD (O /6 )

(, /. )

1 18 19 20 21

)

22 (PCI/L

)

(

WELL WATER HAI GAMMA ZH-65 6

1.33E+01

< L1D (0 /6 )

(. /. )

1 18 19 20 21

)

22 j

(PCI/L

)

(

WELL WATER HAI GAMMA CD-60 6

6.73E+00

< LLD (0 /6 )

(. /. )

1 18 19 20 21 (PCI/L

)

(

)

22 WELL WATER HAI GAMMA K-40 6

7.50E+01

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 1

(PCI/L

)

(

)

22 3

WELL WATER HAI GAMMA BALA-140 6 9.88E+00

< LLD (O /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22 i

WELL WATER HAI GAMMA BE-7 6

6.43E+01

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 I

i (PCI/L

)

(

)

22 6

l WELL WATER HAI GAMMA CR-51 6

7.18E+01

< LLD (0 /6 )

(.

/, )

1 18 19 20 21

__ (PCI/L

)

(

)

22 WELL WATER HAI GAMMA RA-226 6

1.17E+01

< LLD (0 /6 )

(. /. )

1 18 19 20 21 (PCI/L

)

(

)

22 WELL WATER HAI GAMMA I-131 6

1.63E+01

< LLD (O /6 )

(. /. )

1 18 19 20 21 (PCI/L

)

(

)

22 HELL WATER HAI GAMMA HA-22 6

6.53E+00

< LLD (O /6 )

(. /. )

1 18 19 20 21 (PCI/L

)

(

1 22

-138-1 s

RADIOLOGICAL ENVIRONMENTAL MOHITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH JUNE.1982 THROUGH AUGUST,1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMOER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED WELL WATER HAI GAMMA RU-106 6

5.78E+01

< LLD (0 /6 )

(.

/. )

1 18 19 20 21

)

22 (PCI/L

)

(

WEtt WATER HAI GAMMA I-133 6

7.53E+00

< LLD (0 /6 )

(.

/. )

1 18 19 20 21

)

22 e

(PCI/L

)

(

WELL WATER HAI GAMMA CS-137 6

7.00E+00

< LLD (0 /6 )

C. /. )

1 18 19 20 21

)

22 (PCI/L

)

(

CLANS HAI GAMMA CE-144 4

1.07E+02

< LLD (0 /3 )

< LLD (0 /1 )

23 24 25 (PCI/KG(WET))

CLAMS NAI GAMMA AG-110M 4

3.30E+01

< LLD (0 /3 )

< LLD (0/13 23 24 25 (PCI/KG(WET))

CLAMS HAI GAMMA TE-129M 4

7.15E+02

< LLD (0 /3 )

< LLD (0 /1 )

23 24 25 (PCI/KG(WET))

CLANS HAI GAMMA MO-99 4

3.30E+04

< LLD (0 /3 )

< LLD (0/13 23 24 25 (PCI/KG(WET))

CLAMS HAI GAMMA ZRHB-95 4

3.85E+01

< LLD (0 /3 )

< LLD (0 /1 3 23 24 25 i

(PCI/KG(WET))

CLAMS HAI GAMMA CS-134 4

3.20E+01

< LLD (0 /3 )

< LLD

( 0 /1 )

23 24 25

_ (PCI/KG(WET))

CLANS HAI GAMMA CO-58 4

3.80E+01

< LLD (0 /3 )

< LLD (0/13 23 24 25 (PCI/KG(WET))

CLANS HAI GAMMA MH-54 4

3.25E+01

< LLD (0 /3 )

< LLD

( 0 /1 )

23 24 25 (PCI/KG(WET))

CLAMS HAI GAMMA TH-232 4

1.30E+02

< LLD (0 /3 )

< LLD

( 0 /1 )

23 24 25 (PCI/KG(WET))

-139-I

RADIOLOGICAL ENVIRGHMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH JUNE.1982 THROUGH AUGUST,1982 e

FIRST QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED CLAMS HAI GAMMA FE-59 4

9.17E+01

< LLD (0 /3 )

< LLD (0 /1 3 23 24 25 (PCI/KG(WET))

CLANS HAI GAMMA CS-136 4

1.40E+02

< LLD (0 /3 )

< LLD (0 /1 )

23 24 25 (PCI/KG(WET))

CLANS HAI GAMMA TE-132 4

1.50E+03

< LLD (0 /3 )

< LLD (0/13 23 24 25 (PCI/KG(WET))

CLAMS HAI GAMMA ZH-65 4

8.22E+01

< LLD (0 /3 )

< LLD (0 /1 )

23 24 25 (PCI/KG(WET))

CLANS HAI GAMMA CO-60 4

3.90E+01

< LLD (0 /3 )

< LLD (0 /1 3 23 24 25 (PCI/KG(WET))

i CLAMS HAI GAMMA K-40 4

4.30E+02 7.80E+02 (3 /3 3 1.00E+03(1 /1 3 23 24 25 (PCI/KG(WET))

( 5.30E+02 - 9.50E+02)

( 1.00E+03 - 1.00E+03)

CLAMS HAI GAMMA BALA-140 4 1.17E+02

< LLD (0 /3 )

< LLD (0 /1 3 23 24 25 (PCI/KG(WET))

CLANS HAI GAMMA BE-7 4

4.05E+02

< LLD (0 /3 )

< LLD (0 /1 )

23 24 25 i

(PCI/KG(WET))

CLAMS HAI GAMMA CR-51 4

3.22E+02

< LLD (0 /3 )

< LLD (0/11 23 24 25 (PCI/KG(WET))

CLANS HAI GAMMA RA-226 4

6.20E+01

< LLD (0 /3 )

C LLD

( 0 /1 )

23 24 25 4

l (PCI/KG(WET))

j CLAMS HAI GAMMA I-131 4

1.85E+02

< LLD (0 /3 )

< LLD (O /1 3 23 24 25 (PCI/KG(WET))

CLANS HAI GAMMA HA-22 4

3.57E+01

< LLD (0 /3 )

< LLD (0/13 23 24 25 (PCI/KG(WET))

-140-9 3

RADIOLOGICAL ENVIRONMENTAL MOHITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE.1982 THROUGH AUGUST 1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDMS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED CLAMS HAI GAMMA RU-106 4

3.20E+02

< LLD (0 /3 )

< LLD

( 0 /1 )

23 24 25 (PCI/KG(WET))

CLANS HAI GAMMA I-133 4

3.90E+01

< LLD (0 /3 )

< LLD

( 0 /1 )

23 24 25 (PCI/KG(WET))

CLANS HAI GAMMA CS-137 4

3.50E+01

< LLD (0 /3 )

< LLD (0 /1 )

23 24 25 (PCI/KG(WET))

SOIL GELI GAMMA CE-144 10 2.26E+02

< LLD (0 /10 )

(.

/. )

1 2 3 4 5

)

(PCI/F3(DRY))

(

SOIL GELI GAMMA AG-110M 10 7.40E+01

< LLD (0 /10 )

(.

/, )

1 2 3 4 5

)

(PCI/KG(DRY))

(

SOIL GELI GAMMA TE-129M 10 1.29E+03

< LLD (3 /10 )

C. /. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

SOIL GELI GAMMA MO-99 9

2.53E+03

< LLD (O /9 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

SDIL GELI GAMMA ZRHB-95 le 4.13E+01

< LLD (0 /10 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

SOIL GELI GAMMA CS-134 10 3.9EE+01

< LLD (0 /10 )

(,

/. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

SOIL GELI GAMMA CD-58 10 3.41E+01

< LLD (0 /10 )

(,

/. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

SOIL GELI GAMMA MH-54 le 3.15E+01

< LLD (0 /10 3

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

SDIL GELI GAMMA TH-232 10 1 27E+02 3.52E+02 (10 /10 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

( 2.00E+02 - 6.50E+02)

(

)

-141-I a

4 i

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH JUNE.1982 THROUGH AUGUST 1982 FIRST QUARTER

SUMMARY

I SAMPLE TYPE ANALYSIS ISDTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-NEAH(H/ TOTAL)

STATIONS USED i

0F RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED SOIL GELI GAMMA FE-59 10 6.86E+01

< LLD (0 /10 )

(,

/. )

1 2 3 4 5 3

(PCI/KG(DRY))

(

SOIL GELI GAMMA CS-136 10 7.07E+01

< LLD (0 /10 )-

(.

/. )

1 2 3 4 5 1

(PCI/KG(DRY))

(

SOIL GELI GAMMA ZH-65 10 8.15E+01

< LLD (0 /10 )

(,

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

SOIL GELI GAMMA CD-60 10 3.93E+01 6.00E+01 (2 /10 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

( 6.00E+01 - 6.00E+01)

(

SOIL GELI GAMMA K-40 10 4.59E+02 1.37E+03 (9 /10 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

( 7.40E+02 - 2.00E+03)

(

SDIL GELI GAMMA BALA-140 10 7.49E+01

< LLD (0 /10 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

(

3 SDIL GELI GAMMA BE-7 10 5.01E+02

< LLD (0 /10 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

50!L GELI GAMMA ZR-95 1

2.30E+02

< LLD (0 /1 )

(.

/. )

2 (PCI/KG(DRY))

(

)

I SOIL GELI GAMMA HB-95 1

7.10E+02

< LLD (0 /1 )

(.

/. )

2 (PCI/KG(DRY))

(

)

SOIL GELI GAMMA SB-125 10 9.24E+01

< LLD (0 /10 )

(. /. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

SDIL GELI GAMMA CE-141 10 2.13E+02

< LLD CO /10 )

(, /, )

1 2 3 4 5

__ (PCI/KG(DRY))

(

)

SDIL GELI GAMMA RU-103 10 8.69E*01

< LLD (0 /10 )

(, /. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

-142-I

~,-

4 1

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK NUCLEAR GENERATING STATION i

JUNE.1982 THROUGH AUGUST.1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE

' ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAN(H/ TOTAL)

SACKROUND-MEAH(N/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED S0lt GELI GAMMA CR-51 le 4.07E+02

< LLD (0 /10 )

(.

/. )

1 2 3 4 5

)

l (PCI/KG(DRY))

(

SOIL GELI GAMMA RA-226 le 8.42E+01 3.57E+02 (10 /10 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

( 1.70E+02 - 5.80E+02)

(

SOIL GELI GAMMA I-131 le 1.53E+02

< LLD (0 /10 )

(, /. )

1 2 3 4 5 3

(PCI/KG(DRY))

(

SOIL GELI GAMMA HP-239 5

1.24E+05

< LLD (0 /5 )

(.

/. )

1 2 3'

4 5

)

i (PCI/KG(DRY))

(

SOIL GELI GAMMA RU-106 10 2.81E+02

< LLD (0 /10 )

C. /. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

SOIL GELI GAMMA C0-57 10 2.66E+01

< LLD f6 /10 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

a SDIL GELI GAMMA CS-137 le 4.38E+01 4.81E+02 (10 /10 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

( 8.20E+01 - 1.10E+03)

(

)

a j

PASTURE MAI GAMMA CE-144 3

1.33E+02

< LLD (0./3 )

(.

/. )

28 29 30 j

(PCI/KG(WET))

(

)

PASTURE Nt! GAMMA AG-110M 3

4.47E+01

< LLD (0 /3 )

(.

/. )

28 29 30 l

(PCI/KG(WET))

(

)

PASTURE HAI GAMMA TE-129M 3

1.40E+03

< LLD (0 /3 )

(.

/. I 28 29 30 (PCI/KG(WET))

(

3 I

PASIURE MAI GAMMA MD-99 3

2.95E+04

< LLD (0 /3 )

(.

/. )

28 29 30 (PCI/KGtWET))

(

)

PASTURE NAI GAMMA ZRNB-95 3

5.60E+01

< LLD (0 /3 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

-143-I

m g

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION

-JUNE.1982 THROUGH AUGUST.1982 I

FIRST QUARTER

SUMMARY

SAMPLE TYPE AHALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDMS USED 0F RANGE RANGE FOR INDICAIOR MEAN ANALYSES PERFORMED 1

4 1

PASTURE HAI GAMMA CS-134 3

4.23E+01

< LLD (0 /3 )

4. /. )-

28 29 30

)

(PCI/KG(WET))

(

i PASTURE HAI CAMMA CD-58 3

5.47E+01

< LLD (0 /3 )

(. /. )

28 29 30

)

(PCI/KG(WET))

(

PASTURE HAI GAMMA MM-54 3

4.93E+01

< LLD (0 /3 )

(.

/. )

28 29 30

)

(PCI/KG(WET))

(

PASTURE HAI GAMMA TH-232 3

1.90E+02

< LLD (0 /3 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

PASTURE HAI GAMMA FE-59 3

1.43E+02

< LLD (0 /3 )

(.

/. )

28 29 30

)

(PCI/KG(WET))

(

i PASTURE HAI GAMMA CS-136 3

3.00E+02

< LLD (0 /3 )

(. /. )

28 29 30 (PCI/KG(WET))

(

)

L PASTURE HAI GAMMA TE-132 3

1.38E+03

< LLD (0 /3 )

(.

/. )

28 29 30 (PCI/KGtWET))

(

)

PASTURE HAI GAMMA ZH-65 3

1.10E+02

< LLD (0 /3 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

PASTURE HAI GAMMA CD-60 3

4.70E+01

< LLD (0 /3 )

(. /. )

28 29 30 (PCI/KG(WET))

(

)

PASTURE HAI GAMMA K-40 3

8.13E+02 4.00E+03 (2 /3 )

C. /. )

28 29 30 (PCI/KG(WET))

( 3.80E+03 - 4.20E+03)

(

)

1 PASTURE HAI GAMMA BALA-140 3 3.07E+02

< LLD (0 /3 )

(.

/. )

28 29 30

__ (PCI/KG(WET))

(

)

1 PASTURE HAI GAMMA BE-7 3

5.30E+02

< LLD (0 /3 )

(,

/. )

28 29 30 (PCI/KG(WET))

(

)

-144-9 4

x ~.

a-RADIOLOGICAL ENVIRONMENTAL MOHITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH JUNE.1982 THROUGH AUGUST,1982 FIRST CUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(N/ TOTAL)

STATIONS USED OF RANGE RANCE FOR INDICATOR MEAN ANALYSES PERFORMED PAsiURE NAI GAMMA CR-51 3

6.43E+02

< LLD (0 /3 )

(.

/. )

28 29 30

)

(PCI/KG(NET))

(

PASTURE HAI GAMMA RA-226 3

8.13E+C1

< LLD (0 /3 )

(.

/. )

28 29 30

)

(PCI/KG(WET))

(

PASTURE HAI GAMMA I-131 3

5.57E+02

< LLD (0 /3 )

(. /. )

28 29 30

)

(PCI/KG(WET))

(

PASTURE HAI GAMMA NA-22 3

5.30E+01

< LLD (0 /3 )

(.

/. )

28 29 30 (PCI/KG(NET))

(

)

PASTURE HAI GAMMA RU-106 3

4.37E+02

< LLD (0 /3 )

(. /. )

28 29 30 (PCI/KG(WET))

(

)

PASTURE HAI GAMMA I-133 3

4.67E+01

< LLD (0 /3 )

(,

/. )

28 29 30 (PCI/KG(WET))

(

)

PASTURE HAI GAMMA CS-137 3

5.20E+01

< LLD (0 /3 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

SEDIMENT GELI GAMMA CE-144 20 2.17E+02 8.10E+01 (1 /17 )

< LLD (0 /3 3 23 24 25 26 27 (PCI/KG(DRY))

( 8.10E+01 - 8.10E+01) 32 33 SEDIMENT GELI GAMMA AG-110M 20 4.18E+01

< LLD (0 /17 )

< LLD (0 /3 )

23 24 f5 26 27 (PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA TE-129M 20 1.47E+03

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA MO-99 6

6.68E+02

< LLD (0 /5 )

< LLD

( 0 /1 )

23 24 25 32 33 (PCI/KG(DRY))

t SEDINENT GEL 1 GAMMA ZRNB-95 20 4.25E+01

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33

-145-

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING ST*.TIDH JUNE,1982 THROUGH AUGUST,1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEANCH/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED SEDIMENT GELI GAMMA CS-134 20 3.53E+01

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA CD-58 20 3.65E+01

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA MH-54 20 3.66E+01 6.47E+01 (3 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

( 3.50E+01 - 1.20E+02) 32 33 SEDIMENT GELI GAMMA TH-232 20 1.17E+02 3.84E+02 (17 /17 )

3.10E+02(3 /3 )

23 24 25 26 27 (PCI/KG(DRY))

( 1.80E+02 - 7.20E+02)

( 2.60E+02 - 3.70E+02) 32 33

/

SEDIMENT GELI GAMMA FE-59 20 8.52E+01

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA CS-136 20 9.68E+01

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA ZH-65 20 8.66E+01

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA CO-60 20 4.87E+01 5.40E+02 (7 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

( 7.80E+01 - 1.40E+03) 32 33 SEDIMENT GELI GAMMA K-40 20 5.76E+02 5.68E*03 (16 /17 )

5.00E+03(1 /3 )

23 24 25 26 27 (PCI/KG(DRY))

( 2.80E+02 - 1.40E+04)

( 5.00E+03 - 5.00E+03) 32 33 SEDIMENT GELI GAMMA BALA-140 20 9.70E+01

< LLD (0 /17 )

< LLD (0/33 23 24 25 26 27 (PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA BE-7 20 3.51E+02 4.85E+02 (4 /17 )

< LLD (0 /3 )

23 24 25 26 27

_ (PCI/KG(DRY))

( 3.00E+02 - 5.60E+02) 32 33 SEDIMENT GELI GAMMA SB-125 20 8.56E+01

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33

-146-7

1~

t -

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION JUNE.1982 THROUGH AUGUST,1982 FIRST QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN AHALYSES PERFORMED SEDIMENT GELI GAMMA CE-141 20 7.39E*01

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

-32 33 SEDIMENT GELI GAMMA RU-103 20 4.13E+01

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA CR-51 20 3.99E+02

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA RA-226 20 7.47E+01 3.32E*02 (17 /17 )

2.33E+02(3 /3 3 23 24 25 26 27 (PCI/KG(DRY))

( 1.30E+02 - 5.30E+02)

( 1.40E+02 - 3.00E+02) 32 33 SEDIMENT GELI GAMMA I-131 20 2.15E+02

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33

(

SEDIMENT GELI GAMMA HP-239 6

1.99E+05

< LLD (0 /5 )

< LLD

( 0 /1 )

23 24 25 32 33 (PCI/KG(DRY))

SEDIMENT GELI GAMMA RU-106 20 2.77E+02

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA CO-57 20 2.61E+01

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA CS-137 20 3.92E+01 1.89E+02 (11 /17 )

4.10E+01(1 /3 )

23 24 25 26 27 (PCI/KG(DRY))

( 2.90E+01 - 6.50E+02)

( 4.10E+01 - 4.10E+01) 32 33 7

-147-I

TABLE 20 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATIHG STATIDH SEPTEMBER,1982 THROUGH NOVEMBER,1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED VEGETATION GROSS BETA 15 3.33E+01 2.35E+03 (15 /15 )

C. /. )

1 2 3 4 5

)

(PCI/KG(NET))

( l.48E+03 - 3.89E+03)

(

AIR PARTICULATE GROSS ALPHA 51 5.76E-04 1.56E-03 (23 /32 )

1.41E-03(13 /19 )

1 2 3 4 5 (PCI/M3

)

( 5.22E 3.64E-03)

( 4.24E 2.42E-03)

AIP PARTICULATE GROSS BETA 51 5.41E-03 1.68E-02 (27 /32 )

1.61E-02(18 /19 )

1 2 3 4 5 (PCI/M3

)

( 7.93E 2.97E-02)

( 6.94E 2.80E-02)

AIR PARTICULATE S1RONTIUM-89 3

3.22E-04 6.01E-04 (1 /2 )

2.32E-04(1 /1 )

3 5 (PCI/M3

)

( 6.01E 6.01E-04)

( 2.32E 2.32E-04)

AIR PARTICULATE STRONTIUM-90 3

2.33E-04

< LLD (0 /2 )

< LLD (0/13 3 5 (PCI/M3

)

e PRECIPITATION GROSS BETA-SS 24 1.76E+03 1.45E+01 (1 /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

( l.45E+01 - 1.45E+01)

PRECIPITATIDH GROSS BETA-DS 24 1.52E400 4.16E+00 (12 /15 )

3.04E+00(6 /9 )

1 2 3 4 5 (PCI/L

)

( 1.43E+00 - 9.76E*00)~

( l.45E+00 - 7.43E+00)

'~~PRECIPITATIDH TRITIUM 24 1.56E+02 2.65E+02 (2 /15 )

4.81E+02(1 /9 )

1 2 3 4 5 (PC1/L

)

( l.88E+02 - 3.42E+02)

( 4.81E+02 - 4.81E+02)

-148-

e RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH SEPTEM0ER.1982 THROUGH NOVEMBER,1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

OACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED PRECIPITATIDH STRONTIUM-89 24 1.67E+00 6.40E-01 (1 /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

( 6.40E 6.40E-01)

PRECIPITATION STRONTIUM-90 24 1.33E+00

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

AIR IODINE 10 DINE-131 51 2.00E-02

< LLD (0 /32 3'

< LLD (0 /19 3 1 2 3 4 5 (PCI/M3

)

SURFACE WATER GROSS ALPHA-SS 24 1.13E+00

< LLD (0 /21 )

< LLD (0 /3 )

25 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER GROSS ALPHA-DS 24 4.56E-01 1.90E+00 (19 /21')

2.36E+00(3 /3 )

23 24 25 26 27 (PCI/L

)

( 6.60E 2.78E+00)

( 1.76E+00 - 3.03E+00) 32 33 SURFACE WATER GROSS BETA-SS 24 1.42E+00

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER GROSS BETA-DS 24 1.96E+01 1.55E+02 (20 /21 )

2.51E+02(3 /3 )

23 24 25 26 27 (PCI/L

)

( 2.24E+00 - 2.94E+02)

( 2.28E*02 - 2.76E+02) 32 33

"!$URFACE WATER CALCIUM BY AA 24 3.20E-01 2.24E+02 (21 /21 )

3.55E+02(3 /3 )

23 24 25 26 27 (MG/L

)

( 1.10E+00 - 3.50E+02)

( 3.50E*02 - 3.60E+02) 32 33

-149-I

._m RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK NUCLEAR GENERATING STATIDH SEPTEMBER,1982 THROUGH NOVEMBER,1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE NUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED 0F RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED i

SURFACE WATER TRITIUM 24 1.57E+02

< LLD (0 /21 )

< LLD (0 /3 3 23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER RADIUM-226 24 7.25E-02 3.02E-01 (17 /21 3 1.21E-01(3 /3 )*

23 24 25 26 27 (PCI/L

)

( 6.52E 7.25E-01)

( 4.63E 1.90E-01) 32 33 l

l SURFACE WATER RADIUM-228 24 1.20E+00

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 f

SURFACE WATER STRONTIUM-89 24 7.14E-01 3.89E-01 (3 /21 )

< LLD (O /3 )

23 24 25 26 27 (PCI/L

)

( 3.64E 4.18E-01) 32 33 SURFACE WATER STRONTIUM-90 24 5.53E-01

< LLD (0 /21 )

< LLD (0/33 23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER TOTAL URANIUM 24 1.57E-01 1.22E+00 (21 /21 3 1.54E+00(3 /3 )

23 24 25 26 27 (PCI/L

)

( 3.70E 1.98E+00)

( l.13E+00 - 1.83E+00) 32 33 WELL WATER GROSS ALPHA-SS 18 1.14E+00

< LLD (0 /18 )

(, /. )

1 18 19 28 21 (PCI/L

)

(

)

22

~ WELL WATER GROSS ALPHA-DS 18 1.96E+00 4.76E+00 (6./18 )

(. /. )

1 18 19 20 21 (PCI/L

)

( 6.99E 9.32E+00)

(

3 22

-150-l

I J

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH SEPTEMBER.1982 THROUGH NOVEMBER.1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAh(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDMS USED OF RANGE RANGE FOR INDICAIOR MEAN ANALYSES PERFORMED WELL WATER GROSS BETA-SS 18 7.62E-01

< LLD (0 /18 )

(. /. )

1 18 19 29 21

)

22 (PCI/L

)

(

e WELL WATER GROSS BETA-DS 18 8.09E-01 2.74E+00 (18 /18 )

(.

/. )

1 18 19 20 21

)

22 (PCI/L

)

( 1.67E+00 - 4.76E400)

(

WELL WATER POTASSIUM-40 6

8.60E-01 1.41E+00 (5 /6 )

(. /. )

1 18 19 20 21

)

22 (PCI/L

)

( 1.21E+00 - 1.64E+00)

(

WELL WATER TRITIUM 6

1.43E+02

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

3 22 i

WELL WATER RADIUM-226 6

7.24E-02 4.00E-01 (5 /6 )

(. '/. )

1 18 19 20 21 a

(PCI/L

)

( 1.66E 5.73E-01)

(

)

22 i

WELL WATER RADIUM-228 6

8.07E-01

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

3 22 HELL WATER TOTAL URAHIUM 6

2.40E-01 4.87E-01 (6 /6 )

C. /. )

1 18 19 20 21 (PCI/L

)

( 2.6 0 E 7.70 E-01)

(

)

22

~~ CLAMS GROSS ALPHA 12 2.79E+01 1.74E+02 (9 /9 )

6.62E+01(3 /3 3 23 24 25 (PCI/KG(WET))

( 5.03E+01 - 3.57E+02)

( 4.50E+01 - 8.18E+01)

-151-l

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH SEPTEMBER,1982 THROUGH NOVEMBER,1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE AHALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED CLAMS GROSS BETA 12 2.19E+01 9.64E+02 (9 /9 )

1.15E+03(3 /3 )

23 24 25 (PCI/KG(WET))

( 4.17E+02 - 1.33E+03)

( 6.55E+02 - 1.45E+03)

CLAMS CALCIbM BY AA 4

4.40E-01 1.03E+02 (3 /3 )

1.08E+02(1 /1 )

23 24 25 (MG/GM(WET) )

( 6.50E+01 - 1.40E+02)

( 1.08E+02 - 1.08E+02)

CLAMS STRONTIUM-89 4

5.16E401

< LLD (0 /3 )

< LLD (0/13 23 24 25 (PCI/KG(WET))

CLAMS STRONTIUM-90 4

2.62E+01

< LLD (0 /3 )

< LLD (0 /1 3 23 24 25 (PCI/KG(WET))

SOIL GROSS BETA 15 1.74E+03 4.43E+03 (13 /15 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

( 2.54E+03 - 9.46E+03)

(

)

PASTURE GROSS BETA 3

4.66E+01 2.35E+03 (3 /3 )

C. /. )

28 29 30 (PCI/KG(WET))

( 1.28E+03 -'3.13E+03)

(

)

~

PASTURE CALCIUM BY AA 3

8.00E-02 1.89E+02 (3 /3 )

(,

/. )

28 29 30 (NG/GM(WET) )

( 1.63E+02 - 2.23E402)

(

)

7 PASTURE STRONTIUM-89 3

7.07E401

< LLD (0 /3 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

-152-i

RADIOLOGICAL ENVIRONMENTAL MOHITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH SEPTEM8ER,1982 THROUGH NOVEMBER,1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE AHALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICA 10R MEAN ANALYSES PERFORMED PASTURE STRONTIUM-90 3

4.16E+02

< LLD (0 /3 )

(.

/. )

28 29 30 3

(PCI/KG(NET))

(

SEDIMENT GROSS ALPHA 8

3.45E+03 4.83E+03 (2 /7 )

< LLD (0 /1 )

23 24 25 26 27 (PCI/KG(DRY))

( 3.98E+03 - 5.69E+03) 32 33 SEDIMENT GROSS BETA 8

3.89E+03 8.92E+03 (3 /7 )

1.07E+04(1 /1 )

23 24 25 26 27 (PCI/KG(DRY))

( 5.56E+03 - 1.52E+04)

( l.07E+04 - 1.07E+04) 32 33 SEDIMENT STRONTIUM-89 8

1.57E+01 2.40E+01 (7 /7 )

2.28E+01(1 /1 )

23 24 25 26 27 (PCI/KG(DRY))

( l.07E+01 - 6.02E401)

( 2.28E+01 - 2.28E+01) 32 33

~

SEDIMENT STRONTIUM-90 8

3.40E+00

< LLD (0 /7 )

< LLD (0 /1 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 AIR PARTICULATE GELI GAMMA CE-144 50 3.12E-02

< LLD (0 /31 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA AG-110M 51 5.18E-03

< LLD (0 /32 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

7 AIR PARTICULATE GELI GAMMA SR-91 1

3.80E-05

< LLD (0 /1 )

C. /. )

3 (PCI/M3

)

(

)

-153-I

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH SEPTEMBER 1982 THROUGH HOVEMBER,1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAH ANALYSES PERFORMED AIR PARTICULATE GELI GAMMA TE-129M 51 2.34E-01

< LLD (0 /32 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA MD-99 42 3.20E-01

< LLD (0 /28 )

< LLD (0 /14 3 1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA ZRHB-95 3

5.20E-03

< LLD (0 /2 )

< LLD (0 /1 )

3 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA CS-134 51 4.95E-03

< LLD (0 /32 )

< LLD (0 /19 3 1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA CO-58 51 6.11E-03

< LLD (0 /32 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

i AIR PARTICULATE GELI GAMMA MH-54 51 5.55E-03

< LLD (0 /32 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

]

AIR PARTICULATE GELI GAMMA TH-232 51 1.83E-02

< LLD (0 /32 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

~~ AIR PARTICULATE GELI GAMMA FE-59 51 1.31E-02

< LLD (0 /32 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/fl3

)

-154-

RADIOLOGICAL ENVIROHMENTAL MOHITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION a

SEPTEMBER,1982 THROUGH HOVEMBER,1982 3

SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED I

OF RANGE RANGE FOR INDICAIOR MEAM ANALYSES PERFORMED l

AIR PARTICULATE GELI GAMMA CS-136 51 1.41E-02'

< LLD (0 /32 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA ZH-65 51 1.29E-02

< LLD (0 /32 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA CD-60 51 7.73E-03

< LLD (0 /32 )

< LLD (0 /19 3 1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA K-40 51 9.00E-02 3.5dE-01 (2 /32 )

3.80E-01(1 /19 )

1 2 3 4 5 (PCI/M3

)

( 7.70E 6.40E-01)

( 3.80E 3.80E-01) i AIR PARTICULATE GELI GAMMA BALA-140 51 1.92E-02

< LLD (0 /32 )

< LLD (0 /19 3 1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA BE-7 51 6.29E-02 8.81E-02 (11 /32 )

6.92E-02(6 /19 )

1 2 3 4 5 (PCI/M3

)

( 6.10E 1.30E-01)

( 4.80E 9.60E-02) l L

AIR PARTICULATE GELI GAMMA ZR-95 48 1.09E-02

< LLD (0 /30 )

< LLD (0 /18 )

1 2 3 4 5 (PCI/M3

)

""* AIR PARTICULATE GELI GAMMA HO-95 48 7.42E-03

< LLD (0 /30 )

< LLD (0 /18 )

1 2 3 4 5 (PCI/M3

)

-155-I

n RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

GYSTER CREEK HUCLEAR GENERATING STATIDH SEPTEMBER.1982 THROUGH HOVEMBER,1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYS!S ISOTOPE HUMBER LLD INDICATCK-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED AIR PARTICULATE GELI GAMMA 58-125 51 1.46E-02

< LLD (0 /32 3

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA CE-141 51 1.07E-02

< LLD (0 /32 )

< LLD

( 0 /19 )

1 2 3 4 5 (PCI/M3 t)

AIR PARTICULATE GELI GAMMA RU-103 51 6.88E-03

< LLD (0 /32 )

< LLD (0 /19 3 1 2 3 4 5 (PCI/M3

)

4 AIR PARTICULATE GELI GAMMA CR-51 51 6.57E-02

< LLD (0 /32 )

< LLD

( 0 /19 )

1 2 3 4 5 (PCI/M3

-)

AIR PARTICULATE GELI GAMMA RA-226 51 2.07E-02

< LLD (0 /32 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA I-131 51 2.79E-02

< LLD (0 /32 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA HP-239 22 4.45E+01

< LLD (0 /15 )

< LLD (0 /7 )

1 2 3 4 5 (PCI/M3

)

~! AIR PARTICULATE GELI GAMMA RU-106 51 4.73E-02

< LLD (0 /32 )

< LLD (0 /19 )

1 2 3 4 5 (PCI/M3

)

-156-

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

4 OYSTER CREEK NUCLEAR GENERATING STATION SEPTEMBER,1982 THROUGH HOVEMBER,1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(N/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR ]HDICATOR MEAN ANALYSES PERFOR.MED AIR PARTICULATE GELI GAMMA CO-57 44 3.92E-03

< LLD (0 /27 )

< LLD (0 /17 )

1 2 3 4 5 (PCI/M3

)

AIR PARTICULATE GELI GAMMA I-133 1

4.30E-04

< LLD (0 /1 )

(. /. )

3

)

(PCI/M3

)

(

AIR PARTICULATE GEL 1 GAMMA CS-137 51 5.45E-03

< LLD (0 /32 )

< LLD

( ) /19 )

1 2 3 4 5 I

(PCI/M3

)

PRECIPITATION HAI GAMMA CE-144 24 9.29E+01

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION HAI GAMMA AG-110M 24 7.77E+00

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

PRECIPITATIDH HAI GAMMA TE-129M 24 1.59E402

< LLD (O /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION HAI GAMMA MO-99 24 2.79E+03

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5 t

(PCI/L

)

i 1

i

~!PRECIPITATIDH HAI GAMMA ZRHB-95 24 8.01E400

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

-157-

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SUfW1ARY OYSTER CREEK HUCLEAR GENERATING STATIDH SEPTEMBER.1982 THROUGH NOVEMBER,1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED PRECIPITATION HAI GAMMA CS-134 24 7.47E+00

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION HAI GAMMA CO-58 24 8.37E+00

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

PRECIPITATIDH HAI GAMMA MH-54 24 7.52E+00

< LLD (0 /15 )

< LLD (0/93 1 2 3 4 5 (PCI/L

)

PRECIPITATION HAI GAMMA TH-232 24 2.75E+01

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5

' (PCI/L

)

PRECIPITATIDH HAI GAMMA FE-59 24 1.66E401

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION HAI GAMMA CS-136 24 2.21E+01

< LLD (O /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION HAI GAMMA TE-132 24 2.80E+02

< LLD (0 /15 )

< LLD (0 /9 3 1 2 3 4 5 (PCI/L

)

TPRECIPITATION HAI GAMMA ZH-65 24 1.59E+01

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

-158-5

l I

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH I

SEPTEMBER.1982 THROUGH NOVEMBER,1982 l

SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAN(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR IHDICAIOR MEAH ANALYSES PERFORMED l

PRECIPITATION NAI GAMMA CD-60 24 7.78E+00

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5 l

(PCI/L

)

l l

PRECIPITATION HAI GAMMA K-40 24 9.05E+01

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

/

PRECIPITATION HAI GAMMA BALA-I40 24 1.69E+01

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

PRECIPITATIDH HAI GAMMA BE-7 24 8.78E+01

< LLD (0 /15 )

< LLD (0 /9 3 1 2 3 4 5 (PCI/L

)

PRECIPITATIDH HAI GAhdA CR-51 24 1.05E+02

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

PRECIPITATION HAI GAfbtin n-226 24 1.40E+01

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

PRECIPITATIDH HAI GAMMA I-131 24 3.llE+01

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

7 PRECIPITATION HAI GAMMA HA-22 24 7.67E+00

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

-159-I

c-RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

DYSTER CREEK HUCLEAR GENERATING'STATIDH SEPTEMBER,1982 THROUGH NOVEMBER,1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAN(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICAIOR MEAH ANALYSES PERFORMED l

PRECIPITATION HAI GAMMA RU-106 24 7.56E+01

< LLD (0 /15 )

< LL5 (0 /9 )

1 2 3 4 5 (PCI/L

)

PRECIPITATIDH HAI GAMMA I-133 24 8.70E*00

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

PRECIPITATIDH HAI GAMMA CS-137 24 8.07E+00

< LLD (0 /15 )

< LLD (0 /9 )

1 2 3 4 5 (PCI/L

)

SURFACE WATER HAI GAMMA CE-144 24 5.26E+01

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA AG-110M 24 5.33E+00

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 I

(PCI/L

)

32 33 SURFACE WATER HAI GAMMA TE-129M 24 1.07E+02

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA MO-99 24 2.03E+03

< LLD (0 /21 )

< LLV (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33

" SURFACE WATER HAI GAMMA ZRHB-95 24 5.45E+00

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33

-160-5

l l

RADIOLOGICAL ENVIRONMENTAL MOHITORING PROGRAM

SUMMARY

(

OYSTER CREEK HUCLEAR GENERATING STATION SEPTEMBER,1982 THROUGH NOVEMBER 1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAH ANALYSES PERFORMED l

l l

l SURFACE WATER hat GAMMA CS-134 24 5.07E+00

< LLD (O /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA CO-58 24 5.27E+00

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA MM-54 24 4.96E+00

< LLD (0 /21 )

< LLD (0/33 23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA TH-232 24 1.79E+01

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA FE-59 24 1.17E+01

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA CS-136 24 1.51E+01

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA TE-132 24 1.90E+02

< LLD (0 /21 )

< LLD (0 /; J 23 24 25 26 27 (PCI/L

)

32 33

"! SURFACE WATER HAI GAMMA ZH-65 24 1.12E+01

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33

-161-I

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH SEPTEMBER,1982 THROUGH NOVEMBER,1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAN(H/ TOTAL)

BACKROUND-MEAN(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAH ANALYSES PERFCRMED SURFACE WATER HAI GAMMA CD-60 24 5.05E+00

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA K-40 24 7.81E+01

4. ole +02 (16 /21 )

2.90E+02(3 /3 )

23 24 25 26 27 (PCI/L

)

( 6.30E+01 - 2.60E+03)

( 2.50E+02 - 3.10E+02) 32 33 l

l 1

SURFACE WATER HAI GAMMA BALA-140 24 1.13E+01

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA BE-7 24 5.28E+01

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33

$URFACE WATER HAI GAMMA CR-51 24 7.34E+01

< LLD (0 /21 )

< LLD (0 /3 3 23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER.

HAI GAMMA RA-226 24 9.46E+00

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA I-131 24 2.12E+01

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33

~~ SURFACE WATER HAI GAMMA HA-22 24 5.13E+00

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33

-162-El 4

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH SEPTEf1BER,1982 THROUGH NOVEMBER,1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RAHGE RANGE FOR INDICATOR MEAN ANALYSES PERFORNED SURFACE WATER HAI GAMMA RU-106 24 5.22E+01

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 SURFACE WATER HAI GAMMA I-133 24 6.27E+00

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L 1

32 33 SURFACE WATER HAI GAMMA CS-137 24 5.44E+00

< LLD (0 /21 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/L

)

32 33 WELL WATER HAI GAMMA CE-144 6

7.10E+01

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22 WELL WATER HAI GAMMA AG-110M 6

7.12E+00

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22 WELL WATER HAI GAMMA TE-129M 6

1.13E+02

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22 WELL WATER HAI GAMMA MD-99 6

2.85E+02

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22

"!WELL WATER HAI GAMMA ZRHB-95 6

-5.95E+00

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22

-163-

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH SEPTEMBER.1982 THROUGH HOVEMBER,1982 SECOND QUARTER SUt1HARY SAMPLE TYPE ANALYSIS IS0 TOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED 4

WELL WATER HAI GAMMA CS-134 6

6.30E+00

< LLD (0 /6 )

(.

/, )

1 18 19 20 21 (PCI/L

)

(

)

22 i

WELL WATER HAI GAMMA CD-58 6

6.63E+00

< LLD (0 /6 )

(,

/. )

1 18 19 20 21 (PCI/L

)

(

)

22 WELL WATER HAI GAMMA MH-54 6

6.03E+00

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22 WELL WATER HAI GAMMA TH-232 6

2.35E+01

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22 WELL WATER HAI GAMMA FE-59 6

1.27E+01

< LLD (0 /6 )

(. /. )

1 18 19 20 21 (PCI/L

)

(

)

22 WELL WATER HAI GAMMA CS-136 6

1.12E+01

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22 WELL WATER HAI GAMMA TE-132 6

3.75E+01

< L.L D (0 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22

~WELL WATER HAI GAMMA ZH-65 6

1.35E+01

< LLD (0 /6 )

(.

/. )

I 18 19 20 21 (PCI/L

)

(

)

22

-164-1

RADIOLOGICAL ENVIRONMENTAL MOHITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION SEPTEMBER,1982 THROUGH HOVEMBER,1982 SEC0HD QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAH ANALYSES PERFORMED WELL WATER HAI GAMMA CD-60 6

6.73E+00

< LLD (0 /6 )

(.

/. )

1 18 19 20 21

)

22 (PCI/L

)

(

WELL WATER HAI GAMMA K-40 6

7.78E+01

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22 i

WELL WATER HAI GAMMA BALA-140 6 9.52E+00

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22

/

WELL WATER HAI GAMMA BE-7 6

6.55E+01

< LLD (0 /6 )

C. /. )

1 18 19 20 21 (PCI/L

)

(

)

22 r

WELL WATER HAI GAMMA CR-51 6

7.75E+01

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22 WELL WATER HAI GAMMA RA-226 6

1.33E+01 2.65E+01 (2 /6 )

(.

/. )

1 18 19 20 ?!

(PCI/L

)

( 2. 50 E+ 01 - 2.80 E+ 01)

(

)

22 WELL WATER HAI GAMMA I-131 6

1.53E+01

< LLD (0 /6 )

(,

/. )

1 18 19 20 21 (PCI/L

)

(

)

22 i

TWELL WATER HAI GAMMA HA-22 6

6.48E+00

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22

-165-I

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GEHERATING STATION SEPTEMBER.1982 THROUGH HOVEMBER,1982

~

SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED WELL WATER HAI GAMMA RU-106 6

4.57E+01

< LLD (0 /6 )

(.

/. )

1 18 19 20 21

)

22 (PCI/L

)

(

WELL WATER HAI GAMMA I-133 6

2.72E+03

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 1

22 (PCI/L

)

(

WELL WATER HAI GAMMA CS-137 6

7.00E+00

< LLD (0 /6 )

(.

/. )

1 18 19 20 21 (PCI/L

)

(

)

22 CLANS HAI GAMMA CE-144 4

1.19E+02

< LLD (0 /3 )

< LLD (0 /1 )

23 24 25 (PCI/KG(WET))

1 CLANS HAI GAMMA AG-110M 4

2.40E+01

< LLD (O /3 )

< LLD (0 /1 )

23 24 25 (PCI/KG(WET))

CLAMS HAI GAMMA TE-129M 4

5.23E+02

< LLD (0 /3 )

< LLD (0 /1 )

23 24 25 (PCI/KG(WET))

CLANS HAI GAMMA MD-99 4

5.80E+03

< LLD (0 /3 )

< LLD (0 /1 )

23 24 25 (PCI/KG(WET))

I

~ LANS HAI GAMMA ZRHB-95 4

2.33E+01

< LLD (0 /3 )

< LLD (0 /1 )

23 24 25 C

(PCI/KG(WET))

-166-e

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH SEPTEMBER.1982 THROUGH HOVEMBER,1982 SECOND QUARTER SUMf1ARY SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR NEAN ANALYSES PERFORMED CLAMS HAI GAMMA CS-134 4

2.33E+01

< LLD (0 /3 )

< LLD (0 /1 1 23 24 25 (PCI/KG(WET))

l CLAMS HAI GAMMA C0-58 4

2.70E+01

< LLD (0 /3 )

< LLD (0 /1 )

23 24 25 (PCI/KG(WET))

CLAMS HAI GAMMA MH-54 4

2.40E+01

< LLD (O /3 )

< LLD (0 /1 )

23 24 25 (PCI/KG(WET))

i CLANS HAI GAMMA TH-232 4

8.75E+01

< LLD (0 /3 )

< LLD (0 /1 )

23 24 25 (PCI/KG(WET))

CLAMS HAI GAMMA FE-59 4

6.33E+01

< LLD (0 /3 )

< LLD (0 /1 )

23 24 25 *

(PCI/KGCHET))

CLAMS HAI GAMMA CS-136 4

7.43E+01

< LLD (0 /3 )

< LLD (0 /1 )

23 24 25 (PCI/KG(WET))

CLAMS HAI GAMMA TE-132 4

3.45E+02

< LLD (0 /3 )

< LLD (0 /1 )

23 24 25 (PCI/KG(WET))

~! CLAMS HAI GAMMA ZH-65 4

5.68E+01

< LLD (O /3 )

< LLD

( 0 /1 )

23 24 25 (PCI/KG(WET))

-167-l

RADIOLOGICAL ENVIRONMENTAL MONITDRING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION SEPTEMBER.1982 THROUGH HOVEMBER,1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

B A CK ROUN D-M E *.H( H/ T O T A L )

STATIDHS USED OF RANGE RANGE FOR INDICAICR MEAN ANALYSES PERFORMED t

CLAMS HAI GAMMA CD-60 4

2.73E+01

< LLD (0 /3 )

< LLD (0 /1 )

23 24 25 (PCI/KG(WET))

CLANS HAI GAMMA K-40 4

4.28E+02 1.50E+03 (2 /3 )

2.30E+03(1 /1 )

23 24 25 (PCI/KG(WET))

( 1.20E+03 - 1.80E+03)

( 2.30E+03 - 2.30E+03)

CLANS HAI GAMMA BALA-140 4 5.90E+01

< LLD (0 /3 )

< LLD

( 0 /1 )

23 24 25 (PCI/KG(WET))

4 CLANS HAI GAMMA BE-7 4

2.35E+02

< LLD (0 /3 )

< LLD (0 /1 )

23 24 25 (PCI/KG(WET))

CLANS HAI GAMMA CR-51 4

2.25E+02

< LLD (0 /3 )

< LLD

( 0 /1 1 23 24 25 (PCI/KG(WET))

CLANS HAI GAMMA RA-226 4

3.90E+01

< LLD (0 /3 )

< LLD

( 0 /1 )

23 24 25 (PCI/KG(WET))

CLANS NAI GAMMA I-131 4

8.00E+01

< LtD (0 /3 )

< LLD (0 /1 )

23 24 25 (PCI/KG(WET))

ICLANS HAI GAMMA HA-22 4

2.73E+01

< LLD (0 /3 )

< LLD (0 /1 )

23 24 25 (PCI/KG(WET))

-168-5

RADIOLOGICAL ENVIROHMENTAL MONITORING PROGRAM SUMt'ARY OYSTER CREEK HUCLEAR GENERATING STATIDH SEPTEMBER,1982 THROUGH HOVEMBER,1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE ANP. LYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED CLAMS HAI GAMMA RU-106 4

2.40E+02

< LLD (0 /3 )

< LLO (0/13 23 24 25 (PCI/KG(WET))

l CLAMS HAI GAMMA I-133 4

2.73E+01

< LLD (0 /3 )

< LLD (0 /1 )

23 24 25 (PCI/KG(WET))

CLAMS HAI GAMMA CS-137 4

2.73E+01

< LLD (0 /3 )

< LLD (0 /1 )

23 24 25 (PCI/KG(WET))

SOIL GELI GAMMA CE-144 10 2.28E+02

< LLD (0 /10 )

C. /. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

SOIL GELI GAMMA AG-llOM 10 8.99E+01

< LLD (0 /10 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

SDIL GELI GAMMA TE-129M 10 1.23E+03

< LLD (O /10 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

SDIL GELI GAMMA MO-99 10 4.43E+02

< LLD (0 /10 )

(.

/. )

1 2 3 4 5

)

'l (PCI/KG(DRY))

(

"! SOIL GELI GAMMA CS-134 10 4.21E401

< LLD (0 /10 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

-169-I

RADIOLOGICAL EHVIRONMENTAL MOHITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION SEPTEMBER,1982 THROUGH HOVEMBER,1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUHD-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED SOIL GELI GAMMA CO-58 10 3.22E+01

< LLD (0 /10 )

(.

/. )

1 2 3 4 5

)

(PCI/KGCDRY))

(

SDIL GELI GAMMA MH-54 10 3.25E+01

< LLD (0 /10 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

SOIL GELI GAMMA TH-232 10 1.32E+02 2.40E+02 (7 /10 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

( l.60E+02 - 3.50E+02)

(

j SOIL GELI GAMMA FE-59 10 6.60E+01

< LLD (0 /10 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

SOIL GELI GAMMA CS-136 9

4.82E+01

< LLD (0 /9 )

(. /. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

SOIL GELI GAMMA ZH-65 10 8.91E+01

< LLD (0 /10 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

SOIL GELI GAMMA CD-60 10 4.41E+01

< LLD (0 /10 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

~! SOIL GELI GAMMA K-40 10 3.90E+02 9.82E+02 (9 /10 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

( 2.20E+02 - 1.90E+03)

(

)

-170-1 1

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH SEPTEMBER.1982 THROUGH HOVEMBER,1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE AHALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICAIOR MEAM ANALYSES TERFORMED SOIL GELI GAMMA BALA-140 10 6.73E+01

< LLD (0 /10 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

SOIL GELI GAMMA BE-7 10 3.79E+02

< LLD (0 /10 )

(.

/. )

1 2

'3 4 5

)

(PCI/KG(DRY))

(

SOIL GELI GAMMA ZR-95 10 5.96E+01

< LLD (0 /10 )

(.

/. )

1 2 3 4 5 3

(PCI/KG(DRY))

(

SDIL GELI GAMMA HB-95 le 4.32E+01

< LLD (0 /10 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

SOIL GELI GAMMA SB-125 10 1.09E+02

< LLD (0 /10 )

C. /. )

1.

2 3 4 5 (PCI/KG(DRY))

(

)

SOIL GELI GAMMA CE-141 10 6.37E+01

< LLD (0 /10 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

SOIL GELI GAMMA RU-103 10 4.27E+01

< LLD (0 /10 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

"ISOIL GELI GAMMA CR-51 10 3.66E+02

< LLD (O /10 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

(

)

-171-I

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GEHERATING STATIDH SEPTEMBER,1982 THROUGH HOVEMBER,1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED SOIL GELI GAMMA RA-226 10 8.14E+01 2.36E+02 (8 /10 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

( 1.20E+02 - 3.60E+02)

(

SOIL GELI GAMMA I-131 10 9.19E+01

< LLD (0 /10 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

I SOIL GELI GAMMA HP-239 10 1.35E+05

< LLD (0 /10 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

SOIL GELI GAMMA RU-106 10 2.99E+02

< LLD (0 /10 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

Soll GELI GAMMA CO-57 10 2.69E+01

< LLD (0 /10 )

(.

/. )

1 2 3 4 5

)

(PCI/KG(DRY))

(

SOIL GELI GAMMA CS-137 10 4.80E+01 6.56E+02 (10 /10 )

(.

/. )

1 2 3 4 5 (PCI/KG(DRY))

( 4.10E+01 - 1.50E+03)

(

)

PASTURE HAI GAMMA CE-144 3

4.30E+02

< LLD (0 /3 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

~2 PASTURE HAI GAMMA AG-110M 3

1.26E+02

< LLD (0 /3 )

C. /. )

28 29 30 (PCI/KG(WET))

(

3

-172-

RADIOLOGICAL ENVIRDHMENTAL MONITORING PROGP.AM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH SEPTEMBER 1982 THROUGH NOVEMBER,1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE AHALYSIS ISOTOPE HUMBER LLD.

INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED PASTURE HAI GAMMA TE-129M 3

2.23E+03

< LLD (0 /3 )

(.

/. )

28 29 30

)

(PCI/KG(WET))

(

PASTURE HAI GAMMA MO-99 3

6.33E+04

< LLD (0 /3 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

PASTURE HAI GAMMA ZRHB-95 3

1.18E+02

< LLD (0 /3 )

(.

/, )

28 29 30 (PCI/KG(WET))

(

)

PASTURE HAI GAMMA CS-134 3

1.22E+02

< LLD (0 /3 )

(.

/. )

28 29 30 (PCI/KGCWET))

(

)

i PASTURE HAI GAMMA CD-58 3

1.43E+02

< LLD (0 /3 )

(.

/. )

28 29 30 (PCI/KG(NET))

(

}

j PASTURE HAI GAMMA MH-54 3

1.26E+02

< LLD (0 /3 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

PASTURE HAI GAMMA TH-232 3

4.17E+02

< LLD (0 /3 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

i

"! PASTURE HAI GAMMA FF-59 3

3.40E+02

< LLD (0 /3 )

(.

/, )

28 29 30 (PCI/KG(WET))

(

)

t

-173-I

RADIOLOGICAL ENVIRONMENTAL MOHITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH i

SEPTEMBER.1982 THROUGH HOVEMBER,1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEANCH/ TOTAL)

STATI0HS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED l

PASTURE HAI GAMMA CS-136 3

3.77E+02. '< LLD (O /3 )

(.

/. )

28 29 30

)

(PCI/KG(WET))

(

PASTURE HAI GAMMA TE-132 3

3.43E+03

< LLD (0 /3 )

(.

/. )

28 29 30

)

(PCI/KG(WET))

(

PASTURE HAI GAMMA ZH-65 3

2.73E+02

< LLD (0 /3 )

(.

/. )

28 29 30

)

(PCI/KGtWET))

(

PASTURE HAI GAMMA CO-60 3

1.37E+02

< LLD (0 /3 )

(.

/. )

28 29 30 (PCI/KC(WET))

(

)

PASTURE HAI GAMMA K-40 3

1.53E+03

< LLD (0 /3 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

PASTURE HAI GAMMA BALA-140 3 3.60E+02

< LLD (0 /3 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

PASTURE HAI GAMMA BE-7 3

1.22E+03

< LLD (0 /3 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

~ PASTURE HAI GAMMA CR-51 3

1.28E+03

< LLD (0 /3 )

(.

/. )

28 29 30 (PCI/KG(WET))

(

)

-174-

't

1.

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATION SEPTEMBER.1982 THROUGH HOVEMBER,1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/XOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED PASTURE HAI GAMMA RA-226 3

2.60E+02

< LLD (0 /3 )

(.

/. )

28 29 30 3

(PCI/KG(WET))

(

PASTURE HAI GAMMA I-131 3

5.07E+02

< LLD (O /3 )

(.

/. )

28 29 30

)

(PCI/KG(WET))

(

PASTURE HAI GAMMA HA-22 3

1.33E+02

< LLD (0 /3 )

(,

/. )

28 29 30

)

(PCI/KG(WET))

(

PASTURE HAI GAMMA RU-106 3

1.19E+03

< LLD (0 /3 )

(.

/. )

28 29 30

)

(PCI/KG(WET))

(

L PASTURE HAI GAMMA I-133 3

1.43E+02

< LLD (0 /3 )

(.

/. 3 28 29 30

)

(PCI/KG(WET))

(

PASTURE HAI GAMMA CS-137 3

1.30E+02

< LLD (0 /3 )

C. /. )

28 29 30 (PCI/KG(WET))

(

)

SEDIMENT GELI GAMMA CE-144 20 2 72E+02

< LLD (O /17 )

< LLD (0 /3 ) -

23 24 25 26 27 (PCI/KG(DRY))

32' 33

"! SEDIMENT GELI GAMMA AG-110M 20 5.54E+01

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33

-175-l

~. _ _ _

RADIOLOGICAL ENVIROHNENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH SEPTEMBER,3982 THROUGH NOVEMBER,1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS -

ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED SEDIMENT GELI GAMMA TE-129M 20 1.97E+03

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 O

SEDIMENT GELI GAMMA MO-99 17 1.20E+03

< LLD (O /15 )

< LLD (0 /2 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA CS-134 20 6.71E+01

< LLD (0 /17 )

< LLD (O /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA CO-58 20 7.55E+01

< LLD (O /17 )

< LLD (0 /3 )

23 24 25 26 27 i

(PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA MH-54 20 6.21E+01 1.10E+02 (1 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

( 1.10E+02 - 1.10E+02) 32 33 SEDIMENT GELI GAMMA TH-232 20 2.06E+02 4.10E+02 (11 /17 )

3.80E+02(3 /3 )

23 24 25 26 27 (PCI/KG(DRY))

( 1.80E+02 - 7.60E+02)

( 3.40E+02 - 4.00E+02) 32 33 e

SEDIMENT GEL 1 GAMMA FE-59 20 2.08E+02

< LLD (0 /17 )

< LLD (O /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 r

ISEDIMENT GELI GAMMA CS-136 20 1.96E+03

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33

-176-I

- +-

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH SEPTEMBER.1982 THROUGH NOVEMBER.1982 SECOND QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIDHS USED OF RANGE RANGE FOR INDICATOR MEAN ANALYSES PERFORMED SEDIMENT GELI GAMMA ZH-65 20 1.61E+02

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA CO-60 20 7.67E+01 4.93E+02 (7 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

( 4.90E+01 - 1.20E+03) 32 33 l

SEDIMENT GELI GAMMA K-40 20 6.05E+02 6.25E+03 (15 /17 )

1.04E+04(3 /3 )

23 24 25 26 27 (PCI/KG(DRY))

( 7.50E+02 - 1.50E+04)

( 9.10E+03 - 1.20E+04) 32 33 e

SEDIMENT GELI GAMMA BALA-140 20 2.03E+03

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA BE-7 20 8.35E+02 3.80E+02 (1 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

( 3.80E+02 - 3.80E*02) 32 33 SEDIMENT GELI GAMMA ZR-95 20 1.43E+02

< LLD (O /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA HB-95 20 1.44E+02

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 l

7 SEDIMENT GELI GAMMA SB-125 20 1.57E+02

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33

-177-I

, _ _ _ _ _. _ _ = _

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

OYSTER CREEK HUCLEAR GENERATING STATIDH

. SEPTEMBER,1982 THROUGH HOVEMBER,1982 SEC0HD QUARTER

SUMMARY

SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATI0HS USED OF RANGE RANGE FOR INDICAIOR MEAH ANALYSES PERFORMED e

SEDIMENT GELI GAMMA CE-141 20 2.87E+02

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 1

SEDIMENT GELI GAMMA RU 103 20 1.29E+02

< LLD (0 /17 )

< LLD (0 /3 3 23 24 25 26 27 (PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA CR-51 20 5.29E+02

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA RA-226 20 1.21E+02 3.16E+02 (16 /17 )

2.70E+02(3 /3 )

23 24 25 26 27 (PCI/KG(DRY))

( 1.40E+02 - 5.10E+02)

( 2.20E+02 - 3.20E+02) 32 33 i

SEDIMENT GELI GAMMA I-131 20 2.17E+02

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA HP-239 15 7.66E+04

< LLD (0 /13 )

< LLD (0 /2 )

23 24 25 26 27 (PCI/KG(DRY))

32 33 SEDIMENT GELI GAMMA RU-106 20 5.27E+02

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33

" SEDIMENT GELI GAMMA CO-57 20 5.19E+01

< LLD (0 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

32 33

-178-

~

l

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

DYSTER CREEK HUCLEAR GEHERATING STATION SEPTEMBER,1982 TilR00Gil NOVEMBER,1982 SECOND QUARTER SUNMARY SAMPLE TYPE ANALYSIS ISOTOPE HUMBER LLD INDICATOR-MEAH(H/ TOTAL)

BACKROUND-MEAH(H/ TOTAL)

STATIONS USED OF RANGE RANGE FOR INDICATOR MEAH ANALYSES PERFORMED F

SEDIMENT GELI GAMMA CS-137 20 6.70E+01 1.88E+02 (7 /17 )

< LLD (0 /3 )

23 24 25 26 27 (PCI/KG(DRY))

( 3.10E+01 - 3.10E+02) 32 33 4

4 4

enune

-179-

d ANALYSIS OF DATA A statistical analysis was performed on each analytical result during the reporting period according to sample type, station, and analysis to determine which results, if any, were outside the normal or expected range of environmental activities. These ranges were based upon historical data amassed from Oyster Creek's Radiological Environmental Monitoring Program surveys from past years. While these " higher-than-expected" results are somewhat elevated, they are in no way considered to be abnormal. Except where noted, elevated results were not attributed to plant effluents and were, in most cases, naturally occurring isotopes. A discussion of the elevated results follows.

Gamma spectroscopy analysis of air particulate filters revealed higher than usual amounts of K-40 at both indicator and background stations during five of the six months in the sampling period. Since K-40 is a naturally occurring isotope found in a variety of environmental media, the excessive amount on air particulate filters is presumed to be due to dust loading, especially in those sampling locations (e.g. Station

3) near sandy areas. Elevated amounts of K-40 were also found in pasture samples collected during July at Stations 28 and 29 (also adjacent to sandy areas).

K-40 is also found in many types of plants which, in conjunction with the sand, accounts for these elevated results. Surface water samples analyzed for gamma-emitting isotopes during the reporting period also showed infrequent elevated activity of K-40, as did soil samples that were collected. Soil and aquatic sediment samples also showed some slightly higher than normal amounts of Ra-226 and Th-232,

-180 -

both naturally occurring isotopes and not considered to be related to facility effluents. Elevated gross beta activity in both soil and 1

aquatic sediment during the reporting period can be attributed to the elevated K-40, a beta-as well as a gamma-emitter. Ra-226 has a history of being found in regional groundwaters, along with other uranium daughters, which explains the elevated amount of Ra-226 found at well water stations 19 and 21 collected during October.

It is also believed to account for elevated gross alpha activity at Stations 19 and 21 during the same time period. Finally, Be-7 was detected in several media during the six-month sampling period. Elevated amounts were detected in air and aquatic sediment. Being of cosmic origin, the presence of this isotope is not considered to be due to plant operations.

Several fission-product isotopes were detected in various media throughout the reporting period. However, these were either not plant-related and/or already documented. Cs-137 was detected in soil and air particulate samples collected at Station 1 during the fourth quarter. However, no appreciable quantities of this isotope were released from Oyster Creek during the reporting period. Additionally, predominant winds were to the northeast, while Station 1 lies southwest of the plant. For these reasons the Cs-137 detected at station 1 is not considered to be facility-related. For the same reason, a marginally L

elevated amount of Co-60 at Station 1 is not considered to be due to plant effluents.

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During the month of September, Cs-137 was detected in soil at Station 3.

Since no appreciable quantities of Cs-137 were released from the plant during this time, this result is not considered to be related to plant operations.

The presence of several gamma-emitting isotopes found in aquatic sediment in Oyster Creek's discharge canal has already been documented in previous semiannual reports, as well as other publications (Olson et al, 1980). For this reason, Mn-54 activity (June) and Cs-137 activity (August and September) detected at Station 32 at the mouth of the discharge canal are not considered to be abnormal.

An air particulate filter collected at Station A during September revealed a slightly elevated concentration of Sr-89.

Similarly, Station C exhibited higher than normal gross alpha activity and Station H had elevated tritium concentration in precipitation in October. All of these y

stations are background stations and are outside the influence of Oyster Creek. Therefore, these elevated levels of activity are not related to plant operations. Tritium activity in precipitation cellected at Station 2 was observed to be slightly higher than normal. However, as has been previously mentioned, this same condition occurred at a background station (Station H) during the same time period and is therefore not considered to be plant related.

t A clam sample collected from Station 24 in Barnegat Bay during October exhibited an elevated gross alpha activity. Station 24 lies just east of the Oyster Creek discharge canal. Since some radionuclides have previously been detected in sediment in the discharge canal, the

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potential exists that some may find their way, in small quantities, to Barnegat Bay. Any isotopic concentrations in the bay would be concentrated by the clams (Mercenaria mercenaria), themselves being filter feeders. It is possible, then, that this biological characteristic of the clam accounts for the occasionally elevated gross alpha activity.

Finally, a minutely elevated gross beta (soluble) activity was measured in a surface water sample collected at Station 25 during November. The activity measured was 294 pCi/ liter while the maximum predicted activity for this station was 292 pCi/ liter. With a ten per cent analytical error associated with this analysis, the difference between the measured and expected activity is not considered to be' statistically significant and therefore the activity not considered to be abnormal.

In conclusion, no concentrations of radioactivity in the environs of Oyster Creek were found to be abnormal during the reporting period.

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RADIOLOGICAL IMPACT ON MAN Two principle exposure pathways, inhalation and ingestion, are available to gaseous and liquid effluent isotopes, respectively, in the vicinity of Oyster Creek.

Intakes via the inhalation pathway are from gaseous effluents, while the ingestion pathway is via consumption of shellfish from Oyster Creek's discharge canal and Barnegat Bay and consumption of garden vegetables. Additionally, a third means of exposure is from direct radiation from Oyster Creek effluents. The maximum hypothetical exposure to any individual from liquid pathways would occur to someone standing at the offsite boundary on the shore of the discharge canal (direct exposure) consuming shellfish (ingestion).

For purposes of this report this hypothetical individual is designated as Receptor $1.

Maximum exposure due to gaseous pathways (inhalation, ingestion, and direct radiation) would depend on the predominant wind direction and the location of persons living in a given sector with respect to the plant. The direction and distance for this individual is given in Tables 21 and 22.

The following tables represent the offsite dose summary for the two quarters of the six-month reporting period. The information provided was calculated using the models and methodology outlined in NRC Regulatory Guide 1.109 and proposed NRC Regulatory Guide 1.111.

The analysis herein represents the maximum hypothetical liquid and gaseous pathway individual doses (Tables 21, 22, and 23). Also included are the appropriate dose

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limits as given in 10CFR50, Appendix I, the age group, and the receptor location. The semiannual estimated dose and percent of applicable limit complete the offsite dose assessment of maximum hypothetical doses for the semiannual period.

For both quarterly periods, the maximum individual exposures resulting from OCNGS operation from all pathways are well below the USNRC limits of 10 CFR 50, Appendix I and in turn, concentrations in environmental media were well below 1% of concentrations in 10 CFR 20, Appendix B, Table II.

It should be noted that such low offsite doses are probably the result of 1) the average reactor power level being only 60%

of full rated power and 2) the efficient operation of the augmented of f-gas system (AOG) during the period.

Federal reg'ulation 40 CFR 190 requires that doses to any real person from uranium fuel cycle activities (including nuclear power plants) will not exceed 25 mrem / year for the whole body and other organs, with the exception of 75 mrem / year for the thyroid. Jose limits were well below those of 40 CFR 190.

l

~

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TABLE 21

SUMMARY

OF MAXIMUM INDIVIDUAL DOSES FOR THE PERIOD FROM JULY 1, 1982 THROUGH SEPTEMBER 30, 1982 EFFLUENT APPLICABLE ESTIMATED AGE LOCATION ORGAN DOSE GROUP DIST DIR (MREM)

(m)

(TOWARD)

LIQUID TOTAL BODY 1.51 E-5 ADULT RECEPTOR 1 LIQUID GI-TRACT 5.16 E-5 ADULT RECEPTOR 1 NOBLE GAS AIR DOSE (T-MRAD) 4.44 E-7 414 ESE NOBLE GAS AIR DOSE (8-MRAD) 1.44 E-8 4022 ESE NOBLE GAS TOTAL BODY 7.1 E-9 ALL 966 NNE NOBLE GAS SKIN 8.34 E-9 ALL 966 NNE IODINE &

THYROID 2.94 E-7 INFANT 2575 SW PARTICULATE Y

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TABLE 22

SUMMARY

OF MAXIMUM INDIVIDUAL DOSES FOR THE PERIOD FROM OCTOBER 1, 1982 THROUGH DECEMBER 31, 1982 EFFLUENT APPLICABLE ESTIMATED AGE LOCATION ORGAN DOSE GROUP DIST DIR (MREM)

(m)

(TOWARD)

LIQUID TOTAL BODY 3.95 E-6 TEEN RECEPTOR 1 LIQUID GI-TRACT 1.85 E-5 ADULT RECEPTOR 1 NOBLE GAS AIR DOSE ( -MRAD) 3.27 E-7 414 N

NOBLE GAS AIR DOSE (0-MRAD) 1.78 E-8 4022 N

NOBLE GAS TOTAL BODY 3.03 E-13 ALL 966 SE NOBLE GAS SKIN 3.56 E-13 ALL 966 SE IODINE &

THYROID 5.84 E-7 INFANT 2575 SW PARTICULATE

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TABLE 23

SUMMARY

OF MAXIMUM INDIVIDUAL DOSES FOR THE PERIOD FROM JULY 1, 1982 THRCUGH DECEMBER 31, 1982 EFFLUENT APPLICABLE SEMIANNUAL ANNUAL ANNUAL ORGAN ESTIMATED

% APPLIC.

LIMIT DOSE LIMIT (MR)

(MREM)

LIQUID TOTAL BODY 1.91 E-5 6.0 E-4 3.0 LIQUID GI-TRACT 7.01 E-5 7.0 E-4 10.0 NOBLE GAS AIR DOSE (Y-MRAD) 8.16 E-7 8.16 E-6 10.0 NOBLE GAS AIR DOSE (8-MRAD) 3.22 E-8 1.61 E-7 20.0 NOBLE GAS TOTAL BODY 7.10 E-9 1.42 E-7 5.0 NOBLE GAS SKIN 8.34 E-9 5.56 E-8 15.0 ICDINE &

THYROID 8.78 E-7 5.85 E-6 15.0 PARTICULATE

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IV REFERENCES

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Olsen, C.

R., P. E. Biscaye, H. J. Simpson, R. M. Trier, R. F. Kostyk, R. F. Bopp, and Y. H. Li., 1980. " Reactor-released Radionuclides and Fine-grained Sediment Transport and Accumulation Patterns in Barnegat Bay, New Jersey and Adjacent Shelf Waters." Estuarine and Coastal Marine Science 10: 119-142.

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