ML041250418
| ML041250418 | |
| Person / Time | |
|---|---|
| Site: | Oyster Creek |
| Issue date: | 04/29/2004 |
| From: | Swenson C AmerGen Energy Co |
| To: | Document Control Desk, Office of Nuclear Reactor Regulation |
| References | |
| 2120-042-2823, 2130-04-20096 | |
| Download: ML041250418 (100) | |
Text
AmerGenSN AmerGen Energy Company, LLC Oyster Creek US Route 9 South, P.O. Box 388 Forked River, NJ 08731-0388 www.exeloncorp.com An Exelon Company Technical Specification 6.9.1.e April 29, 2004 2130-04-20096 2120-042-2823 U. S. Nuclear Regulatory Commission Attn: Document Control Desk Washington, DC 20555 Oyster Creek Generating Station Facility Operating License No. DPR-1 6 NRC Docket No. 50-219
Subject:
Annual Radiological Environmental Operating Report - 2003 Enclosed is a copy of the Annual Radiological Environmental Operating Report for calendar year 2003, for the Oyster Creek Generating Station. This submittal is made in accordance with Oyster Creek Generating Station Technical Specification 6.9.1.e.
If any further information or assistance is needed, please contact David Fawcett at 609-971-4284.
C. N. Swenson Vice President, Oyster Creek Generating Station CNS/DW/DIF Enclosure cc:
H. J. Miller, Administrator, USNRC Region I P. S. Tam, USNRC Senior Project Manager, Oyster Creek R. J. Summers, USNRC Senior Resident Inspector, Oyster Creek File No. 04004 DeafC
Docket No:
50-219 OYSTER CREEK GENERATING STATION UNIT 1 Annual Radiological Environmental Operating Report 1 January Through 31 December 2003 Prepared By Teledyne Brown Engineering Environmental Services An xelon Company Oyster Creek Generating Station Forked River, NJ 08731 May 2004
Table Of Contents
- 1. Summary and Conclusions..............................
1 II. Introduction..............................
2 A. Objectives of the REMP.............................
2 B. Implementation of the Objectives..............................
3 II. Program Description..............................
3 A Sample Collection.............................
3 B. Sample Analysis.............................
5 C. Data Interpretation..............................
5 D. Program Exceptions.............................
7 E. Program Changes..............................
8 IV. Results and Discussion...............................
9 A. Aquatic Environment..............................
9
- 1. Surface Water.............................
9
- 2. Well Water.............................
9
- 3. Fish 10
- 4. Clams and Crabs...........
10
- 5. Sediment 11 B. Atmospheric Environment...........................
11
- 1. Airborne 11
- a. Air Particulates...........................
11
- b. Airbome Iodine...........................
12
- 2. Terrestrial 12
- a. Vegetation...........................
12 C. Ambient Gamma Radiation
........................ 13 D. Land Use Survey............................
14 V. References...........................
15 i
Appendices Appendix A Radiological Environmental Monitoring Report Summary Tabls Table A-1 Radiological Environmental Monitoring Program Annual Summary for the Oyster Creek Generating Station, 2003 Appendix B Location Designation, Distance & Direction, And Sample Collection &
Analytical Methods Tables Table B-1:
Table B-2:
Table B-3:
Figures Figure B-1:
Figure B-2:
Appendix C Location Designation and Identification System for the Oyster Creek Generating Station Radiological Environmental Monitoring Program - Sampling Locations, Distance and Direction, Oyster Creek Generating Station, 2003 Radiological Environmental Monitoring Program - Summary of Sample Collection and Analytical Methods, Oyster Creek Generating Station, 2003 Oyster Creek Generating Station (OCGS)
Locations of Radiological Environmental Monitoring Program (REMP)
Stations within two miles of the OCGS Oyster Creek Generating Station (OCGS)
Locations of Radiological Environmental Monitoring Program (REMP)
Stations greater than two miles from the OCGS Data Tables - Primary Laboratory Tables Table C-1.1 Table C-1.2 Table C-11.1 Table C-11.2 Table C-111.1 Concentrations of Tritium in Surface Water Samples Collected in the Vicinity of Oyster Creek Generating Station, 2003.
Concentrations of Gamma Emitters in Surface Water Samples Collected in the Vicinity of Oyster Creek Generating Station, 2003.
Concentrations of Tritium in Well Water Samples Collected in the Vicinity of Oyster Creek Generating Station, 2003.
Concentrations of Gamma Emitters in Well Water Samples Collected in the Vicinity of Oyster Creek Generating Station, 2003.
Concentrations of Gamma Emitters in Predator and Bottom Feeder (Fish) Samples Collected in the Vicinity of Oyster Creek Generating ii
Table C-111.2 Table C-IV.1 Table C-V.1 Table C-V.2 Table C-V.3 Table C-V.4 Table C-VI.1 Table C-VII.1 Table C-Vlll.1 Table C-VIII.2 Table C-VIII.3 Table C-IX.1 Figures Figure C-1 Figure C-2 Figure C-3 Figure C-4 Figure C-5 Station, 2003.
Concentrations of Gamma Emitters in Clam and Crab Samples Collected in the Vicinity of Oyster Creek Generating Station, 2003.
Concentrations of Gamma Emitters in Sediment Samples Collected in the Vicinity of Oyster Creek Generating Station, 2003.
Concentrations of Gross Beta in Air Particulate Samples Collected in the Vicinity of Oyster Creek Generating Station, 2003.
Monthly and Yearly Mean Values of Gross Beta Concentrations (E-3 PCI/CU. METER) in Air Particulate Samples Collected in the Vicinity of Oyster Creek Generating Station, 2003.
Concentrations of Strontium in Air Particulate Samples Collected in the Vicinity of Oyster Creek Generating Station, 2003.
Concentrations of Gamma Emitters in Air Particulate Samples Collected in the Vicinity of Oyster Creek Generating Station, 2003.
Concentrations of 1-131 in Air Iodine Samples Collected in the Vicinity of Oyster Creek Generating Station, 2003.
Concentrations of Strontium and Gamma Emitters in Vegetation Samples Collected in the Vicinity of Oyster Creek Generating Station, 2003.
Quarterly TLD Results for Oyster Creek Generating Station, 2003.
Mean Quarterly TLD Results for the Site Boundary, Middle, Special Interest, and Control Locations for Oyster Creek Generating Station, 2003.
Summary of the Ambient Dosimetry Program for Oyster Creek Generating Station, 2003.
Summary of Collection Dates for Samples Collected in the Vicinity of Oyster Creek Generating Station, 2003.
Mean Cobalt-60 Concentration in Clams Oyster Creek Generating Station, 1983 - 2003.
Mean Cobalt-60 Concentration in Aquatic Sediment Oyster Creek Generating Station, 1984 - 2003.
Mean Cesium-137 Concentration in Aquatic Sediment Oyster Creek Generating Station, 1984 - 2003.
Mean Weekly Gross Beta Concentrations in Air Particulates Oyster Creek Generating Station, 2003.
Mean Monthly Gross Beta Concentrations in Air Particulates Oyster Creek Generating Station, 1984 - 2003.
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Figure C-6 Figure C-7 Appendix D Tables Table D-1.1 Table D-1.2 Table D-11.1 Table D-11.2 Table D-111.1 Table D-IV.1 Table D-V.1 Appendix E Tables Table E-1 Table E-2 Table E-3 Table E-4 Table E-5 Table E-6 Mean Quarterly TLD Gamma Dose Oyster Creek Generating Station, 2003.
Mean Quarterly TLD Gamma Dose Oyster Creek Generating Station, 1989 - 2003.
Data Tables - QC Laboratory Concentrations of Tritium in Surface Water Samples Collected in the Vicinity Of Oyster Creek Generating Station, 2003.
Concentrations of Gamma Emitters in Surface Water Samples Collected in the Vicinity of Oyster Creek Generating Station, 2003.
Concentrations of Tritium in Well Water Samples Collected in the Vicinity of Oyster Creek Generating Station, 2003.
Concentrations of Gamma Emitters in Well Water Samples Collected in the Vicinity of Oyster Creek Generating Station, 2003.
Concentrations of Gamma Emitters in Clam Samples Collected in the Vicinity of Oyster Creek Generating Station, 2003.
Concentrations of Gamma Emitters in Sediment Samples Collected in the Vicinity of Oyster Creek Generating Station, 2003.
Concentrations of Gamma Emitters and Strontium in Vegetation Samples Collected in the Vicinity of Oyster Creek Generating Station, 2003.
Inter-Laboratory Comparison Program Analytics Environmental Radioactivity Cross Check Program Teledyne Brown Engineering, 2003 DOE/EML Environmental Radioactivity Cross Check Program Teledyne Brown Engineering, 2003 ERA Environmental Radioactivity Cross Check Program Teledyne Brown Engineering, 2003 MAPEP Environmental Radioactivity Cross Check Program Teledyne Brown Engineering, 2003 ERA Statistical Summary Proficiency Testing Program Teledyne Brown Engineering, 2003 DOE's Mixed Analyte Performance Evaluation Program (MAPEP)
Environmental, Inc., 2003 iv
Summary and Conclusions This report on the Radiological Environmental Monitoring Program conducted for the Oyster Creek Generating Station (OCGS) by AmerGen Energy Company covers the period 01 January 2003 through 31 December 2003. During that time period, 1125 analyses were performed on 983 samples. In assessing all the data gathered for this report and comparing these results with historical data, it was concluded that the operation of OCGS had no adverse radiological impact on the environment.
Surface and well water samples were analyzed for concentrations of tritium and gamma emitting nuclides. No fission or activation products were detected.
Tritium activity was detected at very low levels in both surface water control and indicator stations.
Fish (predator and bottom feeder), clams, crabs, and sediment samples were analyzed for concentrations of gamma emitting nuclides. No fission or activation products were detected in fish, clams, or crabs. Cesium-137 levels detected in sediment were consistent with levels detected in previous years and were due to previous plant releases and fallout from nuclear weapons testing. No other OCGS-produced fission or activation products were detected in sediment.
Air particulate samples were analyzed for concentrations of gross beta and gamma emitting nuclides. Cosmogenic Be-7 was detected at levels consistent with those detected in previous years. No fission or activation products were detected.
High sensitivity 1-131 analyses were performed on weekly air samples. All results were less than the minimum detectable activity.
Strontium-89 and strontium-90 and gamma analyses were performed on quarterly composites of air particulate samples. All strontium-89 and strontium-90 results were below the minimum detectable activity.
Vegetation samples were analyzed for gamma emitting nuclides, strontium-89, and strontium-90. Concentrations of naturally occurring K-40 were consistent with those detected in previous years. Cesium-137 was detected at low levels consistent with those detected in previous years. All strontium-89 results were below the minimum detectable activity. Strontium-90 activity was detected at low levels in both control and indicator stations.
Environmental gamma radiation measurements were performed quarterly using thermoluminescent dosimeters. Levels detected were consistent with those observed in previous years.
1
II.
Introduction The Oyster Creek Generating Station (OCGS), consisting of one boiling water reactor owned and operated by AmerGen Energy Company, is located on the Atlantic Coastal Plain Physiographic Province in Ocean County, New Jersey, about 60 miles south of Newark, 9 miles south of Toms River, and 35 miles north of Atlantic City. It lies approximately 2 miles inland from Barnegat Bay. The site, covering approximately 781 acres, is situated partly in Lacey Township and, to a lesser extent, in Ocean Township. Access is provided by U.S. Route 9, passing through the site and separating a 637-acre eastern portion from the balance of the property west of the highway. The station is about % mile west of the highway and 1% miles east of the Garden State Parkway. The site property extends about 2% miles inland from the bay; the maximum width in the north-south direction is almost 1 mile. The site location is part of the New Jersey shore area with its relatively flat topography and extensive freshwater and saltwater marshlands. The South Branch of Forked River runs across the northern side of the site and Oyster Creek partly borders the southern side.
A Radiological Environmental Monitoring Program (REMP) for OCGS was initiated in 1966. This report covers those analyses performed by Teledyne Brown Engineering (TBE), ICN Pharmaceutical/Global Dosimetry, and Environmental Inc. (Midwest Labs) on samples collected during the period 01 January 2003 through 31 December 2003.
A.
Objectives of the REMP The objectives of the REMP are to:
- 1.
Assess dose impacts to the public from the OCGS operations.
- 2.
To verify in-plant controls for the containment of radioactive materials.
- 3.
To monitor any buildup of long-lived radionuclides in the environment and changes in background radiation levels.
- 4.
To provide reassurance to the public that the program is capable of adequately assessing impacts and identifying noteworthy changes in the radiological status of the environment.
- 5.
Provide data on measurable levels of radiation and radioactive materials in the site environs.
2
- 6.
Evaluate the relationship between quantities of radioactive material released from the plant and resultant radiation doses to individuals from principal pathways of exposure.
- 7.
To fulfill the requirements of the OCGS Offsite Dose Calculation Manual (ODCM) and Technical Specifications.
B.
Implementation of the Objectives The implementation of the objectives is accomplished by:
- 1.
Identifying significant exposure pathways.
- 2.
Establishing baseline radiological data of media within those pathways.
- 3.
Continuously monitoring those media before and during Station operation to assess Station radiological effects (if any) on man and the environment.
Ill.
Program Description A.
Sample Collection Samples for the OCGS REMP were collected for AmerGen Energy Company by on-site personnel and Normandeau Associates, RMC Environmental Services Division (RMC). This section describes the general collection methods used to obtain environmental samples for the OCGS REMP in 2003. Sample locations and descriptions can be found in Tables B-1 and B-2, and Figures B-1 and B-2, Appendix B. The collection procedures are listed in Table B-3.
Aquatic Fnvironment The aquatic environment was evaluated by performing radiological analyses on samples of surface water, well water, fish, clams, crabs, and sediment. One gallon surface water samples were collected monthly from two locations (33 and 94), semi-annually at two locations (23 and 24), and quarterly from three well water locations (1, 37, and 38). Control locations were 94 and 37. All samples were collected in new unused plastic bottles, which were rinsed at least twice with source water prior to collection. Fish samples comprising the flesh of two groups, bottom feeder and predator, were collected semiannually at two locations (93 and 94 (control)). Clams were collected semiannually from three locations (23, 24, and 94 3
(control)). One annual crab sample was collected from one location (93).
Sediment samples were collected at four locations semiannually (23, 24, 33, and 94 (control)).
Atmospheric Environment The atmospheric environment was evaluated by performing radiological analyses on samples of air particulate, airborne iodine, and vegetation.
Airborne iodine and particulate samples were collected and analyzed weekly at seven locations (C, 3, 20, 66, 71, 72, and 73). The control location was C. Airborne iodine and particulate samples were obtained at each location, using a vacuum pump with charcoal and glass fiber filters attached. The pumps were run continuously and sampled air at the rate of approximately two to three cubic feet per minute. The filters were replaced weekly and sent to the laboratory for analysis.
No commercial dairy operations and no dairy animals producing milk for human consumption are located within a 5 mile radius of the plant.
Therefore, vegetation samples were collected in lieu of milk. Vegetation samples were collected, when available, at three locations (35, 36, and 66). Station 36 was the control. All samples were collected in 18" x 24" new unused plastic bags and shipped promptly to the laboratory.
Ambient Gamma Radiation Direct radiation measurements were made using Panasonic Model 814 calcium sulfate (CaSO 4) thermoluminescent dosimeters (TLD). The TLDs were placed on and around the OCGS site and were categorized as follows:
A site boundary ring consisting of 16 locations (1, 51, 52, 53, 54, 55, 56, 57, 58, 59, 61, 62, 63, 64, 65 and 66) near the boundary.
An intermediate distance ring consisting of 16 locations (4, 5, 22, 47, 48, 68, 73, 74, 75, 79, 82, 84, 85, 86, 98, and 99) extending to approximately 5 miles from the site designed to measure possible exposures to close-in population.
Special interest stations consisting of 15 locations (3, 6, 8, 9, 11, 46, 71, 72, 78, 81, 88, 89, 90, 92, and TI) representing special interest areas such as population centers, state parks, etc.
Background (Control) stations consisting of two locations (C and 14) greater than 20 miles distant from the site.
4
Indicator TLDs were placed systematically, with at least one station in each of 16 meteorological compass sectors in the general area of the site boundary. TLDs were also placed in each land-based meteorological sector in the 6 to 8 kilometer range, where reasonable highway access would permit, in areas of public interest and population centers.
Background locations were located greater than twenty miles distant from the OCGS and generally in an upwind direction from the OCGS.
Two TLDs - each comprised of three CaSO4 thermoluminescent phosphors enclosed in plastic - were placed at each location approximately three to eight feet above ground level. The TLDs were exchanged quarterly and sent to ICN/Global Dosimetry for analysis.
B.
Sample Analysis This section describes the general analytical methodologies used by TBE and Midwest Labs to analyze the environmental samples for radioactivity for the OCGS REMP in 2003. The analytical procedures used by the laboratories are listed in Table B-3.
In order to achieve the stated objectives, the current program includes the following analyses:
- 1.
Concentrations of beta emitters in air particulates.
- 2.
Concentrations of gamma emitters in surface and well water, fish, clams, crabs, silt, air particulates, and vegetation.
- 3.
Concentrations of tritium in surface and well water.
- 4.
Concentrations of 1-131 in air iodine cartridges.
- 5.
Concentrations of strontium in air particulates and vegetation.
- 6.
Ambient gamma radiation levels at various locations around the OCGS.
C.
Data Interpretation For trending purposes, the radiological and direct radiation data collected during 2003 was compared with data from past years. For the purpose of this report, OCGS preoperational data was not used due to its collection 35 years ago. Several factors were important in the interpretation of the data:
5
- 1.
Lower Limit of Detection and Minimum Detectable Activity The lower limit of detection (LLD) was defined as the smallest concentration of radioactive material in a sample that would yield a net count (above background) that would be detected with only a 5% probability of falsely concluding that a blank observation represents a "real" signal. The LLD was intended as a before the fact estimate of a system (including instrumentation, procedure and sample type) and not as an after the fact criterion for the presence of activity. All analyses were designed to achieve the required OCGS detection capabilities for environmental sample analysis.
The minimum detectable activity (MDA) is defined above with the exception that the measurement is an after the fact estimate of the presence of activity.
- 2.
Net Activity Calculation and Reporting of Results Net activity for a sample was calculated by subtracting background activity from the sample activity. Since the REMP measures extremely small changes in radioactivity in the environment, background variations may result in sample activity being lower than the background activity which results in a negative number.
An MDA was reported in all cases where positive activity was not detected.
Gamma spectroscopy results for each type of sample were grouped as follows:
For surface and well water 12 nuclides, Mn-54, Co-58, Fe-59, Co-60, Zn-65, Zr-95, Nb-95,1-131, Cs-134, Cs-137, Ba-140, and La-140 were reported.
For fish eight nuclides, K-40, Mn-54, Co-58, Fe-59, Co-60, Zn-65, Cs-1 34, and Cs-I 37 were reported.
For clams eight nuclides, K-40, Mn-54, Co-58, Fe-59, Co-60, Zn-65, Cs-1 34, and Cs-I 37 were reported.
For crabs eight nuclides, K-40, Mn-54, Co-58, Fe-59, Co-60, Zn-65, Cs-1 34, and Cs-1 37 were reported.
For sediment six nuclides, K-40, Mn-54, Co-58, Co-60, Cs-1 34, and Cs-137 were reported.
6
For air particulate six nuclides, Be-7, Mn-54, Co-58, Co-60, Cs-134, and Cs-137 were reported.
For air cartridges one nuclide, 1-131 was reported.
For vegetation four nuclides, K-40,1-131, Cs-134, and Cs-137, were reported.
Means and standard deviations of the results were calculated. The standard deviations represent the variability of measured results for different samples rather than single analysis uncertainty.
D.
Program Exceptions For 2003 the OCGS REMP had a sample recovery rate in excess of 99%.
Exceptions are listed below:
In January 2003, TLDs were vandalized and lost at ODCM required Stations 64 and 68.
From January into March 2003, ODCM required Air Sampler # 66 ran erratically despite weekly maintenance. The average run time for this station for a week was 2 days, 4 hours4.62963e-5 days <br />0.00111 hours <br />6.613757e-6 weeks <br />1.522e-6 months <br />. This station's entire electrical system was changed out on 03/18/2003 which corrected the problem and restored normal station operability. The gross beta LLD for Station 66 was missed due to low sample volume from the air sampler running erratically for the period of 01/23/2003 - 01/25/2003. CAP # 02003-0464 was written to investigate and document this event.
In February 2003, air particulate and air iodine samples from two non-ODCM required air samplers were not collected due to a severe winter blizzard. However, samples from the five required ODCM air samplers were collected during this timeframe.
In February 2003, a revision to the ODCM required TLDs to be in the field in eleven (11) meteorological sectors between a range of 3.73 and 4.97 miles. TLDs were not in place in six of the eleven sectors at the time the revision went into effect. Corrective action included installing TLDs in four of the six required sectors, but TLDs could not be installed in the remaining two sectors due to roadway inaccessibility. ODCM wording will be changed to reflect the inability to gain access to two sectors at this distance. CAP # 02003-0498 was written to investigate and document this event.
In May 2003, vacuum gages at two air sampling stations were found to be 7
sticking when tested at vacuum levels higher than normal operating levels.
These gages were replaced a short time later during the scheduled air sampler semi-annual calibration. CAP # 02003-1068 was written to investigate and document this event.
In July 2003, Air Particulate filters were discovered disintegrated in one ODCM required air sampling station (Station 73) and in two non-ODCM required air samplers. In each case, the particulate samples were lost.
Investigation indicated that the 47 mm particulate filters got wet from a rainstorm and were drawn into the sampler by the relatively high flow rate of the sampler (above 3 CFM). Corrective action was to use a particulate filter that was reinforced. There has been no recurrence. CAP # 02003-1361 was written to investigate and document this event.
In August 2003, ODCM required Air Sampler # 73 was inoperable due to loss of electrical service after a thunderstorm. This station was restored to operation one day after discovery when the local distribution company restored the service. CAP # 02003-1686 was written to investigate and document this event.
In October 2003, ODCM required Air Sampler # 73 failed due to an electrical component failure. Repair and restoration of this station was made within six hours. The gross beta LLD for Station 73 was missed due to low sample volume from the shut down of the air sampler for the period of 10/14/2003 - 10/21/2003. CAP # 02003-2177 was written to investigate and document this event.
In October 2003, TLDs were vandalized and lost at ODCM required Station 78 and at non-ODCM required Station 88.
Each program exception was reviewed to understand the causes of the program exception. Sampling and maintenance errors were reviewed with the personnel involved to prevent recurrence.
The overall sample recovery rate indicates that the appropriate procedures and equipment are in place to assure reliable program implementation.
E.
Program Changes A major rewrite to the ODCM was implemented at the station on February 24, 2003. This revision follows NUREG 1302 format: Offsite Dose Calculation Manual Guidance: Standard Radiological Effluent Controls for Boiling Water Reactors.
8
ICN Pharmaceutical was renamed to Global Dosimetry in 2003.
IV.
Results and Discussion A.
Aquatic Environment 1.
Surface Water Samples were taken via grab sample methodology at two locations (33 and 94) on a monthly schedule. In addition, grab samples were collected semi-annually at two locations (23 and 24). Of these locations 23, 24, and 33, located downstream, could be affected by Oyster Creek's effluent releases. The following analyses were performed:
Tritium Samples from all locations were analyzed for tritium activity (Table C-1.1, Appendix C). Tritium activities were consistent with those detected in previous years.
Gamma Spectrometry Samples from all locations were analyzed for gamma emitting nuclides (Table C-1.2, Appendix C). All nuclides were less than the MDA.
- 2.
Well Water Quarterly samples were composited from monthly grab samples at three locations (1, 37, and 38). Two locations (1 and 38) could be affected by Oyster Creek's effluent releases. The following analyses were performed:
Tritium Quarterly samples from all locations were analyzed for tritium activity (Table C-11.1, Appendix C). No tritium activity was detected. The highest MDA was calculated at <197 pCi/I.
9
Gamma Snectrometry Samples from all locations were analyzed for gamma emitting nuclides (Table C-11.2, Appendix C). All nuclides were less than the MDA.
- 3.
Fish Fish samples comprised of tautog and flounder (bottom feeder) and weakfish, striped bass, white perch, sea bass, bluefish, and puffer (predator) were collected at three locations (33, 93, and 94) semiannually. Locations 93 and 33 could be affected by Oyster Creek's effluent releases. The following analysis was performed:
Gamma Spectrometry The edible portion of fish samples from three locations were analyzed for gamma emitting nuclides (Table C-111.1, Appendix C).
Naturally occurring potassium-40 was found at all stations and ranged from 3,290 to 5,560 pCi/kg wet and was consistent with levels detected in previous years. No fission or activation products were found.
- 4.
Clams and Crabs Clams were collected at three locations (23, 24, and 94) semiannually. Crabs were collected at one location (93) annually.
Locations 23, 24, and 93 could be affected by Oyster Creek's effluent releases. The following analysis was performed:
Gamma Spectrometry The edible portion of clam samples from all three locations were analyzed for gamma emitting nuclides (Table C-111.2, Appendix C).
Naturally occurring potassium-40 was found at all stations and ranged from 610 to 1,340 pCi/kg wet and was consistent with levels detected in previous years. No fission or activation products were found. Historical levels of Co-60 in clams are shown in Figure C-1, Appendix C.
The edible portion of crab samples from one location was analyzed for gamma emitting nuclides (Table C-111.2, Appendix C). Naturally occurring potassiumr-40 was found at a concentration of 2,220 pCi/kg wet and was consistent with levels detected in previous years. No fission or activation products were found.
10
- 5.
Sediment Aquatic sediment samples were collected at four locations (23, 24, 33, and 94) semiannually. Of these locations, stations 23, 24, and 33 located downstream, could be affected by Oyster Creek's effluent releases. The following analysis was performed:
Gamma Spectrometry Sediment samples from all four locations were analyzed for gamma emitting nuclides (Table C-IV.1, Appendix C). Nuclides detected were naturally occurring Be-7 and K-40, and the fission product Cs-1 37.
Beryllium-7 was found in one sediment sample. Location 33 had an average concentration of 224 pCi/kg dry and ranged from <137 to 311 pCi/kg dry. Potassium-40 was found at all stations and ranged from <72 to 14,900 pCikg dry. Concentrations of the fission product Cs-137 were found in one sediment sample. Location 33 had an average concentration of 14 pCi/kg dry and ranged from
<16 to 54 pCi/kg dry. The activity detected was consistent with those detected in previous years (Figure C-3, Appendix C). No other Oyster Creek fission or activation products were found.
Figure C-2, Appendix C graphs Co-60 concentrations in sediment from 1984 through 2003.
B.
Atmospheric Environment
- 1.
Airborne
- a.
Air Particulates Continuous air particulate samples were collected from seven locations on a weekly basis. The seven locations were separated into three groups: Group I represents locations near the OCGS site boundary (20 and 66), Group II represents the locations at an intermediate distance from the OCGS site (71, 72, and 73), and Group IlIl represents the control and locations at a remote distance from OCGS (C and 3). The following analyses were performed:
Gross Beta Weekly samples were analyzed for concentrations of beta 11
emitters (Table C-V.1 and C-V.2, Appendix C).
Detectable gross beta activity was observed at all locations.
Comparison of results among the three groups aid in determining the effects, if any, resulting from the operation of OCGS. The results from the Site Boundary locations (Group I) ranged from <6 to 31 E-3 pCi/M3 with a mean of 14 E-3 pCim. The results from the Intermediate Distance locations (Group II) ranged from <2 to 28 E-3 pCi/m3 with a mean of 14 E-3 pCi/m. The results from the Distant locations (Group ll) ranged from 4 to 35 E-3 pCVm3 with a mean of 14 E-3 pCi/M 3. Comparison of the 2003 air particulate data with previous years data indicate no effects from the operation of OCGS (Figure C-5, Appendix C). In addibon a comparison of the weekly mean values for 2003 indicate no notable differences among the three groups (Figure C-4, Appendix C).
Strontiuim-89 and Strontium-90 Weekly samples were composited quarterly and analyzed for strontium-89 and strontium-90 (Table C-V.3, Appendix C).
No strontium was detected.
Gamma Spactrometry Weekly samples were composited quarterly and analyzed for gamma emitting nuclides (Table C-V.4, Appendix C).
Naturally occurring Be-7 due to cosmic ray activity was detected in all samples. These values ranged from 39 to 68 E-3 pCVm3. All other nuclides were less than the MDA.
- b.
Airborne Iodine Continuous air samples were collected from seven (C. 3, 20, 66, 71, 72, and 73) locations and analyzed weekly for 1-131 (Table C-VI.1, Appendix C). All results were less than the MDA.
- 2.
Terrestrial
- a.
Vegetation Samples were collected from three locations (35, 36, and SSE Sector) when available. The following analyses were 12
performed:
Strontium-89 and Strontium-90 Vegetation samples from all locations were analyzed for concentrations of strontium-89 and strontium-90 (Table C-VII.1, Appendix C). All strontium-89 results were less than the MDA. Strontium-90 was detected in all but seven samples. The values ranged from <2 to 16 pCi/kg wet, which is consistent with historical data.
Gamma Spectrometry Each vegetation sample from locations 35, 36, and SSE Sector were analyzed for concentrations of gamma emitting nuclides (Table C-VIl.1, Appendix C).
Naturally occurring K-40 activity was found in all samples and ranged from 1,590 to 4,630 pCi/I. Cs-1 37 activity detected in six samples was consistent with those detected in previous years. All other nuclides were less than the MDA.
C.
Ambient Gamma Radiation Ambient gamma radiation levels were measured utilizing Panasonic Model 814 (CaSO4) thermoluminescent dosimeters. Forty-four TLD locations were monitored around the site. Results of TLD measurements are listed in Tables C-VIII.1 to C-VIII.3, Appendix C.
Most TLD measurements were below 20 mR/standard quarter, with a range of 6.7 to 21.6 mR/standard quarter. 2003 gamma radiation data from the control location were plotted along with similar data from the Site, Intermediate Distance, and Outer Ring Locations (Figure C-6, Appendix C). Historical ambient gamma radiation data from the control location was plotted along with similar data from the Site, Intermediate Distance and Outer Ring Locations (Figure C-7, Appendix C). The 2003 TLD results are consistent with historical data.
13
Land Use Survey A Land Use Survey, conducted during 2003 around the Oyster Creek Generating Station (OCGS), was performed by Normandeau Associates, RMC Environmental Services Division for Exelon Nuclear. The purpose of the survey was, in part, to determine the location of animals producing milk for human consumption in each of the sixteen meteorological sectors out to a distance of 5 miles from the OCGS. None were observed.
Another purpose of the survey was to determine the location of gardens greater than 500 square feet in size producing broad leaf vegetation, as well as the closest residence within each of the sixteen meteorological sectors. The distance and direction of all locations from the OCGS Reactor Building were positioned using Global Positioning System (GPS) technology. There were no changes required to the OCGS REMP, as a result of this survey. The results of this survey are summarized below.
Distance in Miles from the OCGS Reactor Buildinq Sector Residence Garden*
(Miles)
(Miles) 1 N 1.2 1.3 2 NNE 0.6 1.8 3 NE 0.9 1.6 4 ENE 1.1 5E 1.2 6 ESE 0.7 0.4 7 SE 0.6 0.4 8 SSE 1.3 9S 1.6 2.1 10SSW 1.7 4.3 11 SW 1.7 1.8 12 WSW 2.3 13W 14WNW 15NW 16 NNW 1.5 4.1
- Greater than 500 ft2in size producing broad leaf vegetation 14
V.
References
- 1.
Jersey Central Power and Light Company. Oyster Creek Nuclear Generating Station Operating License and Technical Specifications, Appendix A, DPR-16, April 1969.
- 2.
AmerGen Energy Company, LLC. Oyster Creek Offsite Dose Calculation Manual, Procedure CY-OC-170-301.
- 3.
AmerGen Energy Company, LLC. Oyster Creek Nuclear Generating Station, Updated Final Safety Analysis Report.
- 4.
National Council on Radiation Protection and Measurements, Report No. 93, Ionizing Radiation Exposure of the Population of the United States, 1987.
- 5.
CRC Handbook, Radioecology: Nuclear Energy and the Environment, F. Ward Whicker and Vincent Schultz, Volume I, 1982.
- 6.
National Council on Radiation Protection and Measurements, Report No. 22, Maximum Permissible Body Burdens and Maximum Permissible Concentrations of Radionuclides in Air and Water for Occupational Exposure, (Published as National Bureau of Standards Handbook 69, Issued June 1959, superseding Handbook 52).
- 7.
International Commission on Radiological Protection, Publication 2, Report of Committee II on Permissible Dose for Internal Radiation (1959), with 1962 Supplement Issued in ICRP Publication 6; Publication 9, Recommendations on Radiation Exposure, (1965);
ICRP Publication 7 (1965), amplifying specific recommendations of Publication 9 concerning environmental monitoring; and ICRP Publication 26 (1977).
- 8.
Federal Radiation Council Report No. 1, Background Material for the Development of Radiation Protection Standards, May 13,1960.
- 9.
National Council on Radiation Protection and Measurements,,
Report No. 39, Basic Radiation Protection Criteria, January 1971.
- 10.
National Council on Radiation Protection and Measurements, Report No. 62, Tritium in the Environment, March 1979.
- 11.
National Council on Radiation Protection and Measurements, Report No. 81, Carbon-14 in the Environment, May 1985.
15
- 12.
United States Nuclear Regulatory Commission. Regulatory Guide 4.1, Programs for Monitoring Radioactivity in The Environs of Nuclear Power Plants, Revision 1, April 1975.
- 13.
United States Nuclear Regulatory Commission Branch Technical Position, An Acceptable Radiological Environmental Monitoring Program, Revision 1, November 1979.
- 14.
American National Standards Institute, Inc., Performance, Testing, and Procedural Specifications for Thermoluminescence Dosimetry, ANSI N545-1975.
- 15.
United States Nuclear Regulatory Commission. Regulatory Guide 4.13, Performance, Testing and Procedural Specifications for Thermoluminescence Dosimetry: Environmental Applications, Revision 1, July 1977.
- 16.
United States Nuclear Regulatory Commission. Regulatory Guide 4.15, Quality Assurance for Radiological Monitoring Programs (Normal Operations) - Effluent Streams and the Environment, Revision 1, February 1979.
- 17.
United States Nuclear Regulatory Commission. Regulatory Guide 1.109, Calculation of Annual Doses to Man from Routine Releases of Reactor Effluents for the Purpose of Evaluating Compliance with 10 CFR Part 50, Appendix I, Revision 1, October 1977.
- 18.
NUREG/CR-4068, Summary of Historical Experience with Releases of Radioactive Materials from Commercial Nuclear Power Plants in the United States, 1985.
- 19.
Olsen, C.R., et. al., 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 (1980) 10, 119-142.
- 20.
GPU Nuclear Corporation. 1986 Radiological Environmental Monitoring Report for Oyster Creek Nuclear Generating Station.
May 1987.
- 21.
GPU Nuclear Corporation. 1987 Radiological Environmental Monitoring Report for Oyster Creek Nuclear Generating Station.
May 1988.
16
- 22.
GPU Nuclear Corporation. 1988 Radiological Environmental Monitoring Report for Oyster Creek Nuclear Generating Station.
May 1989.
- 23.
GPU Nuclear Corporation. 1989 Radiological Environmental Monitoring Report for Oyster Creek Nuclear Generating Station.
May 1990.
- 24.
GPU Nuclear Corporation. 1990 Radiological Environmental Monitoring Report for Oyster Creek Nuclear Generating Station.
May 1991.
- 25.
GPU Nuclear Corporation. 1991 Radiological Environmental Monitoring Report for Oyster Creek Nuclear Generating Station.
May 1992.
- 26.
GPU Nuclear Corporation. 1992 Radiological Environmental Monitoring Report for Oyster Creek Nuclear Generating Station.
May 1993.
- 27.
GPU Nuclear Corporation. 1993 Radiological Environmental Monitoring Report for Oyster Creek Nuclear Generating Station.
May 1994.
- 28.
GPU Nuclear Corporation. 1994 Radiological Environmental Monitoring Report for Oyster Creek Nuclear Generating Station.
May 1995.
- 29.
GPU Nuclear Corporation. 1995 Radiological Environmental Monitoring Report for Oyster Creek Nuclear Generating Station.
May 1996.
- 30.
GPU Nuclear, Inc. 1996 Radiological Environmental Monitoring Report for Oyster Creek Nuclear Generating Station. May 1997.
- 31.
GPU Nuclear, Inc. 1997 Radiological Environmental Monitoring Report for Oyster Creek Nuclear Generating Station. May 1998.
- 32.
GPU Nuclear, Inc. 1998 Radiological Environmental Monitoring Report for Oyster Creek Nuclear Generating Station. May 1999.
- 33.
GPU Nuclear, Inc. 1999 Radiological Environmental Monitoring Report for Oyster Creek Nuclear Generating Station. May 2000.
17
- 34.
AmerGen Energy Company, LLC. 2000 Radiological Environmental Monitoring Report for Oyster Creek Generating Station. May 2001.
- 35.
AmerGen Energy Company, LLC. 2001 Radiological Environmental Monitoring Report for Oyster Creek Generating Station May, 2002.
- 36.
AmerGen Energy Company, LLC. 2002 Radiological Environmental Monitoring Report for Oyster Creek Generating Station May, 2003.
- 37.
AmerGen Energy Company, LLC. Oyster Creek Generating Station Radioactive Effluent Release Report, January 1, 2003 through December 31, 2003, March 2004
- 38.
NUREG-1 302, ODCM Guidance: Standard Radiological Effluent Controls for BWR, April 1991 18
APPENDIX A RADIOLOGICAL ENVIRONMENTAL MONITORING REPORT
SUMMARY
TABLE A-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR THE OYSTER CREEK GENERATING STATION, 2003 Name or Facility:
OYSTER CREEK GENERATING STATION DOCKET NUMBER:
50-219 Location of Facility: OCEAN COUNTY, NJ REPORTING PERIOD:
2003 INDICATOR CONTROL LOCATION WIT!! IIIGIIEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEANS MEAN*
MEAN*
STATION #
NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F)
(F)
(F)
NAME NONROUTINE (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT)
(LLD)
MEASUREMENTS SURFACE WATER (PCI/LITER)
TRITIUM 28 3000 176 (2/16)
(<145/193) 173 (1/12)
(<140/200) 187 (0/2)
(<184/<190) 24 INDICATOR BARNEGAT BAY 2.1 MILES SE OF SITE 0
GAMMA MN-54 CO-58 CO-60 FE-59 ZN-65 ZR-95 NB-95 28 is 3
(0/16)
(<2/<8) 15 3
(0/16)
(<21<6) 15 4
(0/16)
(<2/<8) 30 7
(0/16)
(<41<13) 30 7
(0/16)
(<3/<14) 30 6
(0/16)
(<3/<12) 15 4
(0/16)
(<2/<8) 4 (0112)
(<2/<8) 4 (0/12)
(<2/<8) 4 (0/12)
(<2/<1 1) 10 (0/12)
(<41<27) 9 (0112)
(<41<26) 7 (0/12)
(<3/<14) 4 (0/12)
(<2/<8) 4 (0/12)
(<21<8) 4 (0/12)
(<21<8) 4 (0/12)
(<2<1 1) 10 (0/12)
(<4/<27) 9 (0/12)
(<41<26) 7 (0/12)
(<3/<14) 4 (0/12)
(<2/<8) 94 CONTROL GREAT BAY/LITTLE EGd HARBOR 20.0 SSW OF SITE 94 CONTROL GREAT BAY/LITTLE EGG HARBOR 20.0 SSW OF SITE 94' CONTROL GREAT BAY/LITTLE EGG I IARBOR 20.0 SSW OF SITE 94 CONTROL GREAT BAY/LITTLE EGG HARBOR 20.0 SSW OF SITE 94 CONTROL GREAT BAY/LITTLE EGG HARBOR 20.0 SSW OF SITE 94 CONTROL GREAT BAY/LITTLE EGG HARBOR 20.0 SSW OF SITE 94 CONTROL GREAT BAY/LI1TLE EGG HARBOR 20.0 SSW OF SITE
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDAs AND THE POSITIVE VALUES FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)
TABLE A-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR THE OYSTER CREEK GENERATING STATION, 2003 Name oFacility:
OYSTER CREEK GENERATING STATION DOCKET NUMBER:
50-219 Location of Facility: OCEAN COUNTY, NJ REPORTING PERIOD:
2003 INDICATOR CONTROL LOCATION WITII IIIGIIEST ANNUAL AEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN$
MEAN*
MEANS STATION #
NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F)
(F)
(F)
NAME NONROUTINE (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT)
(LLD)
MEASUREMENTS 1-131 CS-134 CS-137 BA.140 LA-140 N/A 7
(0/16)
(<4/<21) 15 3
(0/16)
(<2<6) 18 4
(0/16)
(<n21) 60 18 (0116)
(<10/<37) 15 6
(0/16)
(<'/<14) 6 (0112)
(<3/<12) 3 (0112) 4 (0/12)
(<2/<8) 19 (0/12)
(<8/<40) 6 (0/12)
(<2/<1 1) 13 (0/2)
(<5/<21) 3 (0/12)
(<21<7) 4 (0/12)
(<2/<8) 26 (0/2)
(<14/<37) 9 (0/2)
(<4/<14) 23 INDICATOR BARNEGAT BAY 3.6 MILES SE OF SITE 94 CONTROL GREAT BAY/LITTLE EGG HARBOR 20.0 SSW OF SITE 94 CONTROL GREAT BAY/LITTLE EGG HARBOR 20.0 SSW OF SITE 23 INDICATOR BARNEGAT BAY 3.6 MILES SE OF SITE 23 INDICATOR BARNEGAT BAY 3.6 MILES ENE OF SITE 0
0 0
0 0
WELL WATER (PCI/LITER)
TRIUM 12 2000 186 (0/8)
(<175/<193) 189 (0/4)
(<178/<197) 189 (0/4)
(<178/<197) 37 CONTROL LACEY MUA PUMPING STATION 2.2 MILES NNE OF SITE 0
GAMMA MN-54 CO-58 12 15 3
(0/8)
(<2/<5) 15 3
(0/8)
(<21<5) 3 (0/4)
(<2/<4) 3 (0/4)
(<2/<4) 3 (0/4)
(<2/<5) 3 (0/4)
(<21<5)
I INDICATOR ON-SITE SOUTHERN DOMESTIC WELL 0.1 MILES S OF SITE 38 INDICATOR OCEAN TOWNSHIP MUA PUMP STA 1.3 MILES SSW OF SITE 0
0
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDAS AND THE POSITIVE VALUES FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)
TABLE A-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR THE OYSTER CREEK GENERATING STATION, 2003 Name of Facility:
OYSTER CREEK GENERATING STATION DOCKET NUMBER:
50-219 Location of Facility: OCEAN COUNTY, NJ REPORTING PERIOD:
2003 INDICATOR CONTROL LOCATION WITII HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN' MEAN' MEAN' STATION #
NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F)
(F)
(F)
NAME NONROUTINE (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT)
(LLD)
MEASUREMENTS CO-60 FE.59 ZN-65 ZR-95 NB-95 1131 CS.134 CS-137 15 3
(0/8)
(<1/<6) 30 7
(0/8)
(<31<9) 30 6
(018)
(<41<10) 30 5
(0/8)
(<2<8) 15 3
(0/8)
(<2/<5)
N/A 18 (018)
(<3/<50) is 3
(018)
(<11<4) 18 3
(0/8)
(<2/<5) 3 (0/4)
(<2/<5) 9 (0/4)
(<4/<15) 7 (0/4)
(<4/<10) 5 (0/4)
(<31'7) 3 (0/4)
(<2/<4) 16 (0/4)
(<41<43) 3 (0/4)
(<2/<4) 3 (0/4)
(<2/<4) 3 (0/4)
(<2/<5) 9 (0/4)
(<4/<15) 7 (0/4)
(<c4<10) 6 (0/4)
(<2/48) 3 (0/4)
(<21<5) 18 (0/4)
(<3/<49) 3 (0/4)
(<I/<4) 3 (0/4)
(<2/<5) 37 CONTROL LACEY MUA PUMPING STATION 2.2 MILES NNE OF SITE 37 CONTROL LACEY MUA PUMPING STATION 2.2 MILES NNE OF SITE 37 CONTROL LACEY MUA PUMPING STATION 2.2 MILES NNE OF SITE 38 INDICATOR OCEAN TOWNSHIP MUA PUMP STA 1,3 MILES SSW OF SITE 38 INDICATOR OCEAN TOWNSHIP MUA PUMP STA 1.3 MILES SSW OF SITE 38 INDICATOR OCEAN TOWNSHIP MUA PUMP STA 1.3 MILES SSW OF SITE 38 INDICATOR OCEAN TOWNSHIP MUA PUMP STA 1.3 MILES SSW OF SITE 38 INDICATOR OCEAN TOWNSHIP MUA PUMP STA 1.3 MILES SSW OF SITE
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDAs AND THE POSITIVE VALUES FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)
TABLE A-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR THE OYSTER CREEK GENERATING STATION, 2003.
Name of Facility:
OYSTER CREEK GENERATING STATION DOCKET NUMBER:
50-219 Location of Facility: OCEAN COUNTY, NJ REPORTING PERIOD:
2003 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN*
MEAN' MEANS STATION #
NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWERLIMIT (F)
(F)
(F)
NAME NONROUTINE (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT)
(LLD)
MEASUREMENTS BA.140 LA-140 60 26 (0/8)
(<7/<49) 15 8
(018)
(<3/<15) 25 (0/4)
(<10/<45) 8 (014)
(<3/<15) 26 (0/4)
(<7/<47) 8 (0/4)
(<3/<15) 38 INDICATOR OCEAN TOWNSHIP MUA PUMP STA 1.3 MILES SSW OF SITE 37 CONTROL LACEY MUA PUMPING STATION 2.2 MILES NNE OF SITE 0
0 BOTTOM FEEDER (FISH)
(PCI/KG WET)
GAMMA K.40 3
N/A 5560 (1/1)
(5560)
MN-54 CO-58 CO-60 FE-59 130 23 (011)
(<23) 130 30 (0/1)
(<30) 130 25 (0/1)
(<25) 260 78 (0/1)
(<78) 4480 (22)
(4280/4680) 17 (012)
(<17/<18) 19 (2/2)
(<19/<19) 17 (012)
(<16/<19) 44 (0/)
(<43/<45) 5560 (1/1)
(5560) 23 (0/1)
(<23) 30 (0/1)
(<30) 25 (0/1)
(<25) 78 (0/1)
(<78) 93 INDICATOR DISCHARGE CANAL
- 0. 1 MILES WSW OF SITE 93 INDICATOR DISCHARGE CANAL
- 0. 1 MILES WSW OF SITE 93 INDICATOR DISCHARGE CANAL
- 0. 1 MILES WSW OF SITE 93 INDICATOR DISCHARGE CANAL
- 0. 1 MILES WSW OF SITE 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSW OF SITE 0
0 0
0 0
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDAs AND THE POSITIVE VALUES FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)
TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR THE OYSTER CREEK GENERATING STATION, 2003 Name of Facility:
OYSTER CREEK GENERATING STATION DOCKET NUMIBER:
50-219 Location of Facility: OCEAN COUNTY, NJ REPORTING PERIOD:
2003 INDICATOR CONTROL LOCATION VITII HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN$
MEAN' MEAN*
STATION #
NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F)
(F)
(F)
NAME NONROUTINE (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT)
(LLD)
MEASUREMENTS ZN-65 CS-134 CS-137 260 53 (0/1)
(<53) 130 22 (0/1)
(<22) 150 24 (0/1)
(<24) 37 (0/2)
(<35/<39) 17 (0/2)
(<16/<18) 19 (0/2)
(<18/<20) 53 (011)
(<53) 22 (01)
(<22) 24 (0/1)
(<24) 93 INDICATOR DISCIHARCB CANAL 0.1 MILES WSWOF SITE 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSW OF SITE 93 INDICATOR DISCHARGE CANAL
- 0. I MILES WSW OF SITE 0
0 0
PREDATOR (FISlI)
(PCI/KG WEIR)
GAMMA K-40 13 NIA 4061 (10/10)
(3290/4930) 4083 (313)
(3460/4660) 4083 (3/3)
(3460/4660) 94 CONTROL GREAT BAY/LITTLE EGG HARBOR 20.0 SSW OF SITE 0
MN.54 CO.58 CO-60 FE-59 130 26 (0110)
(<91<73) 130 30 (0/10)
(<10/<85) 130 28 (0/10)
(<9/<75) 260 78 (0110)
(<241<135) 18 (0/3)
(<17/<19) 20 (0/3)
(<18/<21) 18 (0/3)
(<17/<20) 47 (0/3)
(<39/<56) 26 (0/10)
(<9/<73) 30 (0/10)
(<101<85) 28 (0/10)
(<9/<75) 78 (0/10)
(<24/<135) 93 INDICATOR DISCHARGE CANAL
- 0. I MILES WSW OF SITE 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSW OF SITE 93 INDICATOR DISCHARGE CANAL
- 0. I MILES WSW OF SITE 93 INDICATOR DISCHARGE CANAL 0.4 MILF3 WSWOPO 8IT1 0
0 0
0
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDAS AND THE POSITIVE VALUES FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)
TABLE A-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR TIHE OYSTER CREEK GENERATING STATION, 2003 Name of Facility:
OYSTER CREEK GENERATING STATION DOCKET NUIMIBER:
50-219 Location of Facility: OCEAN COUNTY, NJ REPORTING PERIOD:
2003 INDICATOR CONTROL LOCATION WITH IGIHIIEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN' MEAN$
MEAN' STATION N NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F)
(F)
(F)
NAME NONROUTINE (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT)
(LLD)
MEASUREMENTS ZN-65 CS-134 CS-137 CLAMS (PCI/KG WET)
GAMMA K-40 6
260 62 (0/10)
(<11<145) 130 24 (0/10)
(<81<63) 150 28 (0/10)
(<91<78)
N/A 972 (4/4)
(610/1340).
130 16 (0/4)
(<111<24) 130 17 (0/4)
(<13/<21) 130 23 (0/4)
(<12/<51) 260 52 (014)
(<30/<103) 41 (0/3)
(<36/<45) 17 (03)
(<161<18) 19 (0/3)
(<18/<21) 991 (212)
(691/1290) 13 (o0)
(<8/<19) 15 (0o2)
(<81<21) 14 (0/2)
(<11/<18) 43 (0o2)
(<40/<46) 62 (0/10)
(<21/<145) 24 (0/10)
(<81<63) 28 (0/10)
(<9/<78) 1063 (2/2)
(786/1340) 19 (02)
(<151<24) 19 (0/2)
(<17/<21) 32 (0o2)
(<13/<51) 70 (012)
(<381<103) 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSWOF SITE 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSWOF SITE 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSWOF SITE 24 INDICATOR BARNEGAT BAY 2.1 MILES SE OF SITE 24 INDICATOR BARNEGAT BAY 2.1 MILES SEOF SITE 24 INDICATOR BARNEGAT BAY 2.1 MILES SE OF SITE 24 INDICATOR BARNEGAT BAY 2.1 MILES SE OF SITE 24 INDICATOR BARNEGAT BAY 2.1 MILES SE OF SITE 0
0 0
0 0
0 0
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDAs AND THE POSITIVE VALUES FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)
TABLE A-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR THE OYSTER CREEK GENERATING STATION, 2003 Name of Facility:
OYSTER CREEK GENERATING STATION DOCKET NUMBER:
50-219 Location or Facility: OCEAN COUNTY, NJ REPORTING PERIOD:
2003 INDICATOR CONTROL LOCATION WITII HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN' MEAN*
MEAN*
STATION #
NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWERLIMIT (F)
(F)
(F)
NAME NONROUTINE (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT)
(LLD)
MEASUREMENTS ZN-65 CS-134 CS-137 260 45 (0/4)
(<201<101) 130 14 (0/4)
(<10/<17) 150 15 (0/4)
(<11/<19)
CRABS (PCI/KG WET)
GAMMA K-40 I
43 MN-54 CO-SR CO-60 FE-59 N/A 2220 (1/1)
(2220)
N/A 29 (0/I)
(<29)
N/A 33 (011)
(<33)
N/A 31 (0/1)
(<31)
N/A 74 (011)
(<74) 34 (0/2)
(<28/<41) 11 (0/2)
(<5/<17) 12 (0o2)
(<6/<19)
N/A N/A N/A N/A N/A 65 (02)
(<29/<101) 15 (on)
(<14/<17) 17 (0/2)
(<14/<19) 2220 (1/1)
(2220) 29 (0/1)
(<29) 33 (0/1)
(<33) 31 (0/1)
(<31) 74 (0/1)
(<74) 24 INDICATOR BARNEGAT DAY 2.1 MILES SE OF SITE 24 INDICATOR BARNEGAT BAY 2.1 MILES SE OF SITE 24 INDICATOR.
BARNEGAT BAY 2.1 MILES SE OF SITE 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSWOF SITE 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSWOF SITE 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSWOF SITE 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSWOF SITE 93-INDICATOR DISCHARGE CANAL 0.1 MILES WSWOF SITE 0
0 0
0 0
0 0
0
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDAS AND THE POSITIVE VALUES FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)
TABLE A-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR TIHE OYSTER CREEK GENERATING STATION, 2003 Name of Facility:
OYSTER CREEK GENERATING STATION DOCKET NUMBER:
50-219 Location of Facility: OCEAN COUNTY, NJ REPORTING PERIOD:
2003 INDICATOR CONTROL LOCATION WITHI IIGIIEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEANS MEANS MEAN*
STATION N NUMBEROF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F)
(F)
(F)
NAME NONROUTINE (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT)
(LLD)
MEASUREMENTS ZN-65 CS.134 CS-137 N/A 55 (0/1)
(<55)
N/A 27 (0/1)
(<27)
N/A 29 (0/1)
(<29)
N/A N/A N/A 55 (0/1)
(<55) 27 (0/1)
(<27) 29 (0/1)
(<29) 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSW OF SITE 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSWOF SITE 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSWOF SITE 0
0 0
SEDIMENT (PCI/KG DRY)
GAMMA Be-7 8
C~o K-40 MN-54 CO-58 CO-60 N/A 163 (1/6)
(<84/111)
N/A 1447 (5/6)
(<72/4720)
N/A 13 (0/6)
(<9/< 8)
N/A 14 (0/6)
(<g/<21)
N/A 16 (0/6)
(<10/<30) 240 (0/2)
(<161/<319) 14200 (2/2)
(13500/14900) 24 (0/2)
(<17/<21) 25 (0n)
(<18/<32) 23 (0/2)
(<21/<26) 240 (0/2)
(<161/<319) 14200 (2/2)
(13500/14900) 24 (0/2)
(<17/<21) 25 (0o2)
(<18/<32) 23 (0/2)
(<21/<26) 94 CONTROL GREAT BAY/LITTLE EGG HARBOR 20.0 SSW OF SITE 94 CONTROL GREAT BAY/LITTLE EGG HARBOR 20.0 SSW OF SITE 94 CONTROL GREAT BAY/LITTLE EGG HARBOR 20.0 SSW OF SITE 94 CONTROL GREAT BAY/LITTLE EGG HARBOR 20.0 SSW OF SITE 94 CONTROL GREAT BAY/LITTLE EGG HARBOR 20.0 SSW OF SITE 0
0 0
0
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDAS AND THE POSITIVE VALUES FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)
TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR THE OYSTER CREEK GENERATING STATION, 2003 Name of Facility:
OYSTER CREEK GENERATING STATION DOCKET NUMBER:
50-219 Location of Facility: OCEAN COUNTY, NJ REPORTING PERIOD:
2003 INDICATOR CONTROL LOCATION WVITII IIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN*
MEAN*
MEAN*
STATION #
NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F)
(F)
(F)
NAME NONROUTINE (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT)
(LLD)
MEASUREMENTS CS-134 CS-137 150 12 (0/6)
(<8/<17) 180 14 (116)
(<10/<19) 20 (0/2)
(<17/<23) 25 (0/2)
(<211<29) 20 (0/2)
(<17/<23) 25 (012)
(<21/<29) 94 CONTROL GREAT BAY/LITTLE EGG HARBOR 20.0 SSW OF SITE 94 CONTROL GREAT BAY/LITTLE EGG HARBOR 20.0 SSW OF SITE 0
0 AIR PARTICULATE (E-3 PCI/CU.METER)
GROSS BETA 361 10 14 (304/309)
(<2/31) 14 (52152)
(4/35) 14 (51/51)
(5/31) 20 INDICATOR FINNINGER FARM 0.7 MILES E OF SITE 0
SR-89 SR-90 GAMMA BE-7 28 28 N/A 4.2 (0124)
(<l.01<9.5)
N/A 1.3 (0o24)
(<0.2/.1)
N/A 49 (24124)
(39/68) 3.8 (0/4)
(<1.2/<6.9) 1.5 (0/4)
(<0.21<2.8) 49 (4/4)
(41/54) 5.2 (0/4)
(<1.3/<9.5) 1.6 (0/4)
(<0.3/<3.1) 55 (4/4)
(42168) 66 INDICATOR OCGS DISCHARGE CANAL 0.4 MILES SE OF SITE 66 INDICATOR OCGS DISCHARGE CANAL 0.4 MILES SE OF SITE 20 INDICATOR FINNINGER FARM 0.7 MILES E OF SITE 0
0 28 0
MN-54 CO-58 N/A 0.3 (014)
(<0.1/<0.5)
N/A 0.3 (0124)
(<0.09/<0.6) 0.2 (0/4)
(<0.07/<0.3) 0.2 (0/4)
(<0.09/<0.3) 0.4 (0/4)
(<0.2/<0.5) 0.4 (0/4)
(<0.2/<0.6) 66 INDICATOR OCGS DISCHARGE CANAL 0.4 MILES SE OF SITE 66 INDICATOR OCGS DISCHARGE CANAL 0.4 MILES SE OF SITE 0
0
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDAs AND THE POSITIVE VALLED.
FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)
TABLE A-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR THE OYSTER CREEK GENERATING STATION, 2003 Name of Facility:
OYSTER CREEK GENERATING STATION DOCKET NUMBER:
50-219 Location of Facility: OCEAN COUNTY, NJ REPORTING PERIOD:
2003 INDICATOR CONTROL LOCATION WITII IIIGIIEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEANO MEAN MEAN*
STATION #
NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F)
(F)
(F)
NAME NONROUTINE (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT)
(LLD)
MEASUREMENTS CO-60 CS-134 CS 137 N/A 0.3 (0/24)
(<0.11<0.5) 50 0.2 (0124)
(<0.07/<0.4) 60 0.3 (0/24)
(<0.07/<0.5)
AIR IODINE (E-3 PCI/CU.METER) 1.131 01 VEGETATION (PCI/KG WET)
SR-89 361 18 18 18 SR-90 GAMMA K-40 70 6
(0/309)
(<11<32)
N/A 10 (0/111)
(<W<19)
NIA 7
(7/11)
(<3/16)
N/A 3031 (11/11)
(1590/4470) 60 38 (0/1 1)
(<17/<60) 0.2 (0/4)
(<0.081<0.4) 0.2 (0/4)
(<0.06/<0.3) 0.2 (0/4)
(<0.08/<0.3) 5 (0/52)
(<1/<13) 12 (on)
(<8/<20) 7 (4n)
(<2/16) 2987 (7n)
(1950/4630) 42 (0/7)
(<13/<60) 0.4 (0/4)
(<0.3/<0.5) 0.3 (0/4)
(<0.1/<0.4) 0.3 (0/4)
(<0.21<0.4) 8 (0/52)
(<1/<32) 12 (0o7)
(<8/<20) 8 (3/6)
(<3/16) 3234 (5/5)
(2210/4470) 42 (0/7)
(<13/<60) 66 INDICATOR OCGS DISCHARGE CANAL 0.4 MILES SE OF SITE 66 INDICATOR OCGS DISCHARGE CANAL 0.4 MILES SE OF SITE 66 INDICATOR OCGS DISCHARGE CANAL 0.4 MILES SE OF SITE 66 INDICATOR OCGS DISCHARGE CANAL 0.4 MILES SE OF SITE 36 CONTROL
'U PICKI FARM 23.1 MILES NW OF SITE 35 INDICATOR OCGS DISCHARGE CANAL 0.4 MILES ESE OF SITE SSE SECTOR INDICATOR OCGS DISCHARGE CANAL 0.4 MILES SSE OF SITE 36 CONTROL U-PICK FARM 23.1 MILES NW OF SITE 0
0 0
0 0
0 0
1-131 0
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDAS AND THE POSITIVE VALUES FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)
TABLE A-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR THE OYSTER CREEK GENERATING STATION, 2003 Name of Facility:
OYSTER CREEK GENERATING STATION DOCKET NUMNIBER:
50-219 Location of Facility: OCEAN COUNTY, NJ REPORTING PERIOD:
2003 INDICATOR CONTROL LOCATION VITII IHGIIEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEANS MEAN*
MEAN*
STATION #
NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F)
(F)
(F)
NAME NONROUTINE (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT)
(LLD)
MEASUREMENTS CS-134 CS-137 60 10 (0/1 1)
(.c2k21) 80 19 (6/11)
(<121<22) 8 (07)
(<4/<18) 9 (on7)
(<4/<22) 10 (0/6)
(<2k21) 20 (4/6)
(<26/20) 35 INDICATOR OCGS DISCHARGE CANAL 0.4 MILES ESE OF SITE 35 INDICATOR OCGS DISCHARGE CANAL 0.4 MILES ESE OF SITE 0
0 DIRECT RADIATION TLD-QUARTERLY (MILLI-ROENTGEN/STD.QUARTER 182 N/A 13.9 (174/174)
(8.9/21.5) 14.4 (818)
(10.9/17.2) 18.9 (4/4)
(16.6121.5) 55 INDICATOR OCGS SWITCIIYARD 0.3 MILES W OF SITE 0
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDAS AND THE POSITIVE VALUES FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)
Intentionally Left Blank
APPENDIX B LOCATION DESIGNATION, DISTANCE & DIRECTION, AND SAMPLE COLLECTION & ANALYTICAL METHODS
TABLE B-1:
Location Designation and Identification System for the Oyster Creek Generating Station Sample Medium APT =
AlO
=
WWA =
VEG =
SWA =
AQS =
Air Particulate Air Iodine Well Water Vegetation Surface Water Aquatic Sediment Clam= Clam TLD = Thermoluminescent Dosimetry Fish
= Fish Crab = Crab Station Code Station's Designation Distance Distance from the OCGS in miles Azimuth Azimuth with respect to the OCGS in degrees Description Meteorological sector in which the station is located and a narrative description B-1
TABLE B-2:
Radiological Environmental Monitoring Program - Sampling Locations, Distance and Direction, Oyster Creek Generating Station, 2003 Sample Modllm TLD WWA APT, AIO, TLD TLD TLD TLD TID TLI)
APT, AIO TLD SWA, CLAM, AQS SWA, CLAM, AQS SWA, AQS, FISH VEG VEG VWA WVWA Station roda I
1 3
4 5
6 8
9 C
11 14 20 22 23 24 33 35 36 37 38 Distance 0.4 0.1 0.2 6.0 4.6 4.2 2.1 2.3 2.0 24.7 8.2 20.8 0.7 1.6 3.6 2.1 0.4 0.4 23.1 22 1.6 Azimuth 219 209 349 97 213 353 13 177 230 313 152 2
95 145 64 101 123 111 319 18 197 Ilascdriptinn SW of site at OCGS Fire Pond, Forked River, NJ On-site southern domestic well at OCGS, Forked River, NJ On-site northern domestic well at OCGS, Forked River, NJ East of site, near old Coast Guard Station, Island Beach State Park SSW of site, Route 554 and Garden Parkway, Bamegat, NJ North of site, at Garden State Rest Area. Forked River, NJ NNE of site, Lane Place, behind SL Pius Church, Forked River, NJ South of site, Route 9 at the Waretown Substation, Waretown, NJ SW of site, where Route 532 and the Garden State Parkway meet, Waretown, NJ NW of site, JCP&L office In rear parking lot, Cookstown, NJ SSE of site, 80e and Anchor Streets. Harvey Cedars, NJ North of site, Larrabee Substation on Randolph Road, Lakewood, NJ East of site, on Finninger Farm on south side of access road, Forked River, NJ SE of site, on Long Silver Way, Skippers Cove, Waretown, NJ ENE of site, Bamegat Bay off Stouts Creek, approximately 400 yards SE of Flashing Ught 1-East of site, Bamegat Bay, approximately 250 yards SE of
'Flashing LUght 3-ESE of site, east of Route 9 Bridge In OCGS Discharge Canal ESE of site, east of Route 9 and north of the OCGS Discharge Canal, Forked River, NJ NW of site, at 'U-Pick' Farm, New Egypt, NJ NNE of Site, off Boox Road at Lacey MUA Pumping Station, Forked River, NJ SSW of Site, on Route 532, at Ocean Township MUA Pumping Station, Waretown, NJ B-2
TABLE B-2:
Radiological Environmental Monitoring Program - Sampling Locations, Distance and Direction, Oyster Creek Generating Station, 2003 Sample Madlum TLD TLD TLD TLD TLD TLD TLD TID TLD TLD TLD TLD TLD TLD TLD TLD TLD APT, AlO, TLD, VEG TLD APT, AIO, TLD Station 46 47 48 51 52 53 54 55 56 57 58 59 61 62 63 64 65 66-68 71 Distance 4mgM 5.6 4.6 4.5 0.4 0.3 0.3 0.3 0.3 0.3 0.2 0.2 0.3 0.3 0.2 0.2 0.3 0.4 0.4 1.3 1.6 Azimuth 323 26 189 358 333 309 288 263 249 206 188 166 104 83 70 48 19 133 265 164 npsrrdpln NNW of site, on Lacey Road near Forked River, NJ NNE of site. Harbor Inn Road and Bayville,. J South of site, at Brooks and Schoolhouse Roads, Bamegat, NJ North of site, on the access road to Forked River site, Forked River. NJ NNW of site, on the access road to Forked River site. Forked River, NJ NW of site, at sewage lift station on the access road to the Forked River site. Forked River. NJ WNW of site, on the access road to Forked River site, Forked River, NJ West of site, on Southern Area Stores secuwy fence, west of OCGS Switchyard, Forked River, NJ WSW of site, on utility pole east of Southern Area Stores, west of the OCGS Switchyard, Forked River, NJ SSW of site, on Southern Area Stores access road, Forked River. NJ South of site, on Southern Area Stores access road, Forked River, NJ SSE of site, on Southern Area Stores access road, Waretown, NJ ESE of site, on Route 9 south of OCGS Mairt Entrance.
Forked River, NJ East of site, on Route 9 at access road to OCGS Main Gate, Forked River, NJ ENE of site, on Route 9, between main gate and OCGS North Gate access road, Forked River, NJ NE of site, on Route 9 at entrance to Finninger Farm, Forked River, NJ NNE of site, on Route 9 at Intake Canal Bridge, Forked River, NJ SE of site, east of Route 9 and south of the OCGS Discharge Canal, Inside fence, Waretown, NJ West of sie, on Garden State Parkway at mie marker 71.7, Lacey Township, NJ SSE of site, on Route 532 at the Waretown Municipal Building, Waretown, NJ
- The garden at station 66 failed due to excessive and persistent rainfall In the spring of 2003. Vegetables from a garden In the SSE Sector were substituted.
B-3
TABLE B-2.
Radiological Environmental Monitoring Program - Sampling Locations, Distance and Direction, Oyster Creek Generating Station, 2003 Sample U
sdkzm APT, AIO, TLD APT, A1O. TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD FISH. CRAB SWA. AQS. CLAM.
FISH TLD TLD TLD Station CAds 72 73 74 75 78 79 81 82 84 Distance Azimuth 1.9 1.8 1.8 2.0 1.8 2.9 3.5 4.4 4.4 25 108 88 71 2
160 201 36 332 85 3.9 86 5.0 88 6.6 89 6.1 90 6.3 92 9.0 93 0.1 94 20.0 98 1.3 99 1.5 T1 0.4 250 224 125 108 75 46 242 198 292 310 219 11~rripfln NNE of site, on Lacey Road at Knights of Columbus Hall, Forked River, NJ ESE of site, on Bay Parkway. Sands Point Harbor, Waretown, NJ East of site, Orlando Drive and Penguin Court, Forked River.
NJ ENE of site, Beach Blvd. and Maui Drive, Forked River, NJ North of site, 1514 Arient Road, Forked River. NJ SSE of site, Hightide Drive and Bonita Drive. Waretown, NJ SSW of site, on Rose HlI Road at Intersection with Barnegat Boulevard. Bamegat, NJ NE of site, Bay Way and Clairmore Avenue, Lanoka Harbor, NJ NNW of site, on Lacey Road, 1.3 miles west of the Garden State Parkway on siren pole. Lacey Township, NJ WSW of site, on Route 532, just east of Wells Mills Park, Waretown, NJ SW of site, on Route 554,1 miie west of the Garden State Parkway, Barnegat, NJ SE of sihe, eastern end of 34 Street, Bamegat Ught. NJ ESE of site, Job Francis residence, Island Beach State Park ENE of site, parking lot A-5, Island Beach State Park NE of site, at Guard Shack/Toll Booth, Island Beach State Park WSW of site, OCGS Discharge Canal between Pump Discharges and Route 9. Forked River, NJ SSW of site, In Great Bayl-ttle Egg Harbor WNW of site. on Garden State Parkway at mile marker 72.3.
Lacey Township. NJ NW of site, on Garden State Parkway at mile marker 72.8.
Lacey Township, NJ SW of site, at OCGS Fire Pond, Forked River, NJ B4
TABLE B-3:
Radiological Environmental Monitoring Program - Summary of Sample Collection and Analytical Methods, Oyster Creek Generating Station, 2003 Sample Analysis Sampling Method Collection Procedure Number Sample Size Analytical Procedure Number Medium Surface Water Gamma Spectroscopy Grab Sample.
2120-IMP-4522.06 Oyster Creek sample 1 gallon TBE, PRO-042-5 Determination of gamma emitting collection procedure - surface water radioisotopes Env. Inc, GS-01 Determination of gamma emitters by
_gamma soectroscoov Surface Water Tritium Grab Sample.
2120-IMP4522.06 Oyster Creek sample 1 gallon TBE, PRO-052-35 Determination of tritium In water by liquid collection procedure - surface water scintillation Env. Inc, T.02 Determination of tritium in water (direct
_method)
Well Water Gamma Spectroscopy Monthly samples 2120-IMP-4522.10 Oyster Creek sample 1 gallon TBE, PRO-42-5 Determination of gamma emitting composited quarterly.
collection procedure - well water radioisotopes Env. Inc., GS-01 Determination of gamma emitters by camma spectroscoov Well Water Tritium Monthly samples 2120-IMP.4522.10 Oyster Creek sample 1 gallon TBE, PRO-052-35 Determination of tritium In water by liquid composited quarterly, collection procedure - well water scintillation Env. Inc.. T.02 Determination of tritium in water (direct method)
Fish Gamma Spectroscopy Seml-annual samples 2120-IMP-4522.14 Oyster Creek sample 1000 grams (wet)
TBE. PRO-042-5 Determination of gamma emitting collected via hook and collection procedure - fish radioisotopes lne technique and traps Env. Inc., GS-O1 Determination of gamrna emitters by
_amma sWectroscoov Clams and Gamma Spectroscopy Semi-annual and annual 2120-IMP-4522.16 Oyster Creek sample 1000 grams (wet)
TBE. PRO-042-5 Determination of gamma emitting Crabs samples collected using collection procedure - clams and crabs radioisotopes dam tongs and traps.
Env. Inc., GS-01 Determination of gamma emitters by gamma spectroscopv Sediment Gamma Spectroscopy Semi-annual grab 2120-IMP-4522.03 Oyster Creek collection 1000 grams (dry)
TBE. PRO-042-5 Determination of gamma emitting samples procedure - aquatic sediment radioisotopes Env. Inc, GS-01 Determination of gamma emitters by gamma soectroscoDv B-5
TABLE B-3:
Radiological Environmental Monitoring Program - Summary of Sample Collection and Analytical Methods, Oyster Creek Generating Station, 2003 Sample Analysis Sampling Method Collection Procedure Number Sample Size Analytical Procedure Number Medium Air Particulates Gross Beta One-week composite of 2120-IMP-4522.05 Oyster Creek sample I filter (approximately TBE. PRO-032-10 Gross beta and/or alpha activity in air continuous air sampling collection procedure - air particulate and air 700 cubic meters particulate filters (direct count method) through glass fiber filter iodine weekly) paper Env. Inc., AP-02 Determination of gross alpha and/or gross beta In air particulate filters Air Particulates Gamma Spectroscopy Quarterly composite of 2120-IMP-4522.05 Oyster Creek sample 13 filters TBE, PRO-042-5 Determination of gamma emitting each station collection procedure - air particulate and air (approximately 9100 radioisotopes Iodine cubic meters)
Env. Inc.. GS-01 Determination of gamma emitters by gamma spectroscoov Air Particulates Strontium-89190 Quarterly composite of 2120-IMP-4522.05 Oyster Creek sample 13 filters TBE, PRO-032-24R Determination of radlostrontium In each station collection procedure - air particulate and air (approximately 9100 composited air particulate filters Iodine cubic meters)
Air Iodine Gamma Spectroscopy One-week composite of 2120-IMP-4522.05 Oyster Creek sample 1 filter (approximately TBE, PRO-042-5 Determination of gamma emitting continuous air sampling collection procedure - air particulate and air 700 cubic meters radioisotopes through charcoal filter Iodine weekly)
Env. Inc., 1-131-02 Determination of 1-131 in charcoal canisters by gamma spectroscopv (batch method)
Vegetation Gamma Spectroscopy Grab sample during 2120-4MP-4522.04 Oyster Creek sample 1000 grams TBE. PRO-042-5 Determination of gamma emitting growing season.
collection procedure - food products and radioisotopes broadleaf vegetables Env. Inc., GS-01 Determination of gamma emitters by gamma soectroscoov Vegetation Strontum-89190 Grab sample during 2120-iMP-452Z.04 Oyster Creek sample 1000 grams TBE, PRO-032-23R Determination of radiostrontium in growing season.
collection procedure - food products and feedstuff and forage broadleaf vegetables TLD Thermoluminescence Quarterly TLDs 2120-IMP-4522.02 Oyster Creek sample 2 dosimeters ICN Pharmaceutical/Global Dosimetry, Inc.
Dosimetry comprised of two collection procedure - Thermoluminescent Panasonic 814 Dosimetry (containing 3 each CaSOi elements)
B-6
Figure B-1 Oyster Creek Generating Station (O CGS)
Locations of Radiological Environmental Monitoring Program (RENp)
Stations within two miles of the OCGS B-7
Figure B-2 Oyster Creek Generating Station (OCGS)
Locations of Radiological Environnental Monitoring Program (REMP)
Stations greater than 2 miles from the O CGS B-8
APPENDIX C DATA TABLES PRIMARY LABORATORY
TABLE C-1.1 CONCENTRATIONS OF TRITIUM IN SURFACE WATER SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF PCI/LITER i2 SIGMA COLLECTION PERIOD 23 24 33 94 JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC
< 183
< 179 181 +/- 6
< 190
< 184 187 +/- 8
< 161
< 187 193 i 117
< 156
< 169
< 186 182 +/- 92
< 160
< 188
< 175
< 171
< 145
< 164
< 193 200 +/- 121
< 188
< 172
< 176
< 144
< 140
< 173
< 190
< 195
< 146 173 +/- 42 MEAN*
173 +/- 30
^ THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES C-1
TABLE C-I.2 CONCENTRATIONS OF GAMMA EMITTERS IN SURFACE WATER SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMA STC COLLECTION Mn-54 Co-58 Fe-59 CO-60 Zn-65 Zr-95 Nb-95 1-131 Cs-134 Cs-137 Ba.140 La-140 PERIOD 23 JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC MEAN*
C) r)
24 JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC
<'4
< 4 (10
< 8
< 5 (21
<'4
'C 37
< 14
<3
' 3
<6
<3
<5
<5
<3
'5
<3
<3
<14
<'4 3 +/-2 4 +/-2 8*6 4*+/-3 68+/-4 6*+/-3 4 +/-3 13*+/-22 3*+/-1 3 +/-1 26*+/-33 9*+/-14
<(
<4
< 5
<3
( 14
< 2 2
<(23
<(4
<(4
< 8
<4 8
< 7
' 4 8 6
<3
( 4
' 17
<'6 MEAN*
3*+/-2 3*+/-2 7*+/-4 3*+/-2 6*+/-5 6*+/-3 3*+/-2 10*+/-10 3*i2 3*+/-2 20*+/-8 7*+/-2
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES
TABLE C-1.2 CONCENTRATIONS OF GAMMA EMITTERS IN SURFACE WATER SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF PCIILITER +/- 2 SIGMA STC COLLECTION PERIOD 33 JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC Mn-54 Co-58 Fe-59 Co-60 Zn-65 Zr-95 Nb-95 1-131 Cs-134 Cs-137 Ba-140 La-140
< 3
< 4
< 7
< 2
< 2
< 4
< 3
<c4
< 8
< 2
< 2
< 4
< 3
< 3
< 8
< 2
<c2
< 4
< 3
< 3
< 6
< 4
< 4
< 8
< 5
< 4
< 9
< 8
< 6
< 13
< 3
<c3
< 6
< 4
< 4
< 9
< 4
< 7
< 2
< 3
< 4
< 8
< 2
< 4
< 3
< 7
< 2
< 4
< 3
< 6
< 4
< 8
< 4
< 10
< 8
< 14
<c3 IC6
< 4
< 9
< 6
< 3
< 6
< 4
< 6
< 4
< 6
< 7
< 8
< 12
'C5
< 7
< 4
< 7
< 2
< 6
< 4
< 5
< 2
< 4
< 3
< 8
< 2
< 4
< 3
< 4
< 4
< 5
< 5
< 6
< 8
< 11
<c3
< 5
< 4
< 7
< 3
<c4
< 19
< 2
< 2
< 13
<4
< 4
< 16
< 2
< 2
< 10
< 3
< 4
< 20
< 2
< 2
< 12
< 3
< 3
< 13
< 4
<c4
< 16
<4
< 5
< 19
< 6
< 7
< 31
'c3
<c3
<'14
<4
< 5
< 19
< 5
< 4
< 5
< 3
< 6
< 4
< 4
< 5
< 7
< 12
'44
< 7 MEAN*
4 +/-3 3*+/-3 7*+/-5 4 +/-4 7 +/-6 6*+/-5 4 +/-3 6*+/-4 3*+/-3 4*+/-3 17*+/-11 6+/-
5 JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC
< 2
< 2
< 9
< 2
< 2
< 4
<c4
< 4
< 8
< 4
< 4
< 8
< 4
<c4
< 9
< 3
< 3
< 6
< 3
< 3
< 6
< 3
< 3
< 6
< 4
< 4
< 8
< 8
< 8
< 17
< 6
<c5
< 27
<c5
<q5
< 10
< 3
< 2
< 4
< 4
< 3
< 3
< 3
< 3
< 4
< 8
< 11
< 5
< 8
< 4
< 8
< 8
< 8
< 6
< 7
< 6
< 8
< 16
< 26
< 7
< 3
< 4
< 7
< 7
< 8
< 5
< 5
< 5
< 7
< 14
< 8
< 8
< 2
< 3
< 2
< 6
< 4
< 5
< 4
< 6
< 4
< 9
< 3
< 6
< 3
< 4
< 3
< 4
< 4
< 6
< 8
< 12
< 4
< 9
< 5
< 7
<c2
<c2
< 4
< 4
< 3
< 3
< 3
< 3
< 4
< 7
< 5
< 4
< 2
< 8
< 2
< 14
< 4
< 17
< 4
< 19
< 4
< 24
< 3
< 17
< 3
< 13
< 3
< 12
< 4
< 17
< 8
< 40
< 5
< 22
< 5
< 25
< 2
< 5
< 5
< 6
< 8
< 6
< 4
< 4
< 5
< 11
< 11
< 6 MEAN*
4*+/-3 4*+/-3 10*+/-13 4 +/-5 9*+/-12 7*+/-6 4*+/-3 6*+/-5 3*+/-3 4*+/-3 19*+/-17 6+/-
5
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES
TABLE C-11.1 CONCENTRATIONS OF TRITIUM IN WELL WATER SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMA COLLECTION PERIOD 1
37 38 JAN - MAR APR - JUN JUL - SEP OCT - DEC MEAN'
< 191
< 176
< 189
< 186
< 197
< 178
< 188
< 194
< 188
< 175
< 193
< 187 186 +/- 13 189 i 17 186 i 15
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES C4
TABLE C-11.2 CONCENTRATIONS OF GAMMA EMITTERS IN WELL WATER SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF PCIILITER +/- 2 SIGMA STC COLLECTION PERIOD Mn-54 1
JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC MEAN*
37 JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC MEAN*
' 3
<'3
' 5
< 2 Co-58 Fe-59 CO-60 Zn-65 Zr-95 3
<'6
< 3 5
<5 2
<'3
<3
<'5
<4 4
< 8
<6
<'9
<'7 2
<'6
'2 4
' 4 Nb-95
' 3
' 3
' 4
' 2 3*+/-1
' 4
' 2
' 4
<'2 1-131 Cs-1 34 Cs-137 Ba-140 La-140
<'4
<'2
<'3 3*1
' 4
' 2
' 4
' 2 6*+/-4
<'9
<'4
' 7
<'15 3 +/-3
' 5
' 2
' 4
' 4 6*i4
<'9
<'4
<'7
' 10 5*+/-3
<'7
' 3
<'6
<'4
' 8
' 4
' 7
' 50 17 +/- 44
' 11
'4
' 7
<'43
' 3
<'3
<18
<'2
<'3
<13
' 4
' 4
'22
'c2
<'2
' 49
<'6
<'3
' 7
<'15 7 +/- 10
< 10
<'3
' 6
< 15 3*+/-2
' 4
<'2
' 3
<'2 3 +/-2
' 4
'c2
' 3
< 2 25 +/- 32
<'27
< 10
< 19
<'45 3 +/-2 3 +/-3 9 +/-9 3*+/-3 7*i5 5*+/-4 3 +/-3 16*+/-36 3*+/-2 3*+/-2 25*+/-30 8*+/-10
' THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES
TABLE C-11.2 CONCENTRATIONS OF GAMMA EMITTERS IN WELL WATER SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF PCI/LITER i 2 SIGMA STC COLLECTION PERIOD Mn-54 Co-58 Fe-59 Co-60 Zn-65 Zr-95 Nb-95 1-131 Cs-134 Cs-137 Ba-140 La-140 38 JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC MEAN*
<4
<5
<9
<4
<8
<8
<4
<12
<4
<4
<27
<9
<2
<2
<8
<3
<7
<2
<2
<3
<1 c2
<7
<3
<4
<4
<9
<4
<10
<8
<5
<8
<4 c5
<23
<7
<2
<2
<5
<1
<4
<4
<2
<49
<2
<2
<47
<13 3 +/- 3 3 +/- 3 8 +/- 4 3 +/- 3 7 +/- 5 6 +/- 6 3 +/- 3 18 +/- 42 3
- 3 3 +/- 3 26 +/- 33 8 +/- 8
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES
TABLE C-111.1 CONCENTRATIONS OF GAMMA EMITTERS IN PREDATOR & BOTTOM FEEDER (FISH)
SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF PCIlKG WET +/- 2 SIGMA STC COLLECTION PERIOD K-40 Mn-54 Co-S6 Fe-59 CO-60 Zn-65 Cs-134 Ca-137 33 33 93 93 93 93 93 33 33 33 PREDATOR 04/15 - 04115103 04116 -04/16/03 04/16 - 04116103 04/16 -04116/03 04/17 -04117/03 09/23 - 09/23103 09/23 - 09)23/03 09/24 -09/24/03 09/24 - 09/24103 09/24 - 09/24/03 4210 4050 4930 4100 4590 3800 3290 4010 3870 3760
+/- 679
+/- 373
+/- 369
+/- 431
- 1090
+/- 341
+/- 195
+/- 646
+/- 318
- 522
<36
< 19
< 18
< 23
<73
< 12 9
< 37
< 14
<24
< 47
< 22
<20
< 27
< 85
< 13
< 10
<35
< 16
< 25
< 123
< 53
< 51
<60
< 185
<31
< 24
< 100
< 37
< 121
<33
<20
< 19
< 23
< 75
< 12 9
<31
< 15
<39
< 82
< 44
< 42
<49
( 145
<25
< 21
<74
<32
( 105
<36
< 18
< 17
< 22
<63
< 10 (8
< 37
< 15
< 19
<38
< 20
<20
<23
< 78
< 12
( 9
< 41
< 15
< 20
)
MEAN*
4061 +/- 907 26 +/- 38 30 +/- 45
< 30 78 +/- 104 28 +/- 38 62 +/- 79
<53 24 i 33 28 +/- 41 93 BOTTOM FEEDER 05/20 - 05)20)03 5560 +/- 467
< 23
<78
<25
< 22
< 24 94 PREDATOR 06/11 - 06/11/03 09/23 - 09)23103 09123 - 09/23/03 4130 +/- 336 4660 +/- 365 3460 +/- 363
< 17
< 19
< 19 MEAN*
4083 +/- 1203 18 +/- 2
< 18
< 21
< 21 20 +/- 4
< 19
< 19 19 +/- 1
< 39
< 56
< 48 47 +/- 16
< 45
< 43 44 +/- 4
< 17
< 20
< 19 18 +/- 3
< 16
< 19 17 +/- 5
< 36
<45
< 43 41 +/- 9
< 35
( 39 37 +/- 6
< 16
< 18
< 17
< 18
<21
< 19 17 +/- 3 19 +/- 3 94 BOTTOM FEEDER 04/16 - 04116/03 06)11 06/11/03 4280 +/- 325 4680 +/- 395
< 17
< 18
< 16
< 18
< 18
<20 MEAN' 4480 +/- 566 17 +/- 3 17
- 3 19 t 3
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES
TABLE CI111.2 STC COLLECTION PERIOD 23 CLAMS CONCENTRATIONS OF GAMMA EMITTERS IN CLAM AND CRAB SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF PCI/KG WET +/-2 SIGMA K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 Cs.134 Cs-137 04/14 - 04115103 09123 - 09/23/03 MEAN*
24 CLAMS 04/14 09122 o
94 CLAMS 60 04/15 09124
- 04114103
- 09/22103 MEAN*
- 04/15/03
- 09/24103 MEAN' 1150 +/- 167 610 +/- 231 880 +/- 764 1340 +/- 236 786 +/- 425 1063 +/- 783 691 i 181 1290 +/- 288 991 +/- 847 2220 +/- 478
< 11
' 15 13 i 6
' 15
( 24 19
- 13 (8
' 19 13 i 16
< 29
< 13
< 17 15
- 6
< 17
' 21 19
- 6 c 8
< 21 15
- 19
' 33
'30
'38 34 +/- 12
< 38
< 103 70 +/- 92
( 40
<46 43 +/- 9
< 74
< 12
< 16 14 +/- 6
< 13
< 51 32 +/- 54
< 11
< 18 14
- 9
( 31
< 20
< 30 25 +/- 14
< 29
< 101 65 +/- 102
< 28
< 41 34
- 19
< 55
< 10
< 15 12 +/- 7
' 14
< 17 15 +/- 4 (5
( 17 11 +/- 17
< 11
< 15 13 +/- 6
( 14
( 19 17 +/- 7
<6
( 19 12 +/- 18 93 CRABS 09/25 - 10/01/03
< 27
< 29
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES
TABLE C-IV.1 STC COLLECTION PERIOD 23 04/15/03 09/23103 MEAN*
CONCENTRATIONS OF GAMMA EMITTERS IN SEDIMENT SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF PCI/KG DRY +/-2 SIGMA Be-7 K-40 Mn-54 Co-58 Co-60 Cs-134 Cs-137
<213
< 84 148 i 183 24 04/14/03 09/22/03 MEAN*
< 110
< 124 117 +/- 20 311 +/- 131
< 137 224 +/- 248 763 +/- 237 1660 +/- 152 1212 +/- 1269
<72 664 +/- 266 368 +/- 837 4720 +/- 246 802 +/- 202 2761 + 5541
< 18
< 9 13 i 12
<9
< 15 12 +/- 8
< 13
< 13 13 +/- 0.4
< 21
< 8 15 +/- 18
<11
<15 13 +/- 5
<16
<14 15 +/- 2
< 16
< 10 13 +/- 9
< 10
<30 20 +/- 28
< 14
< 15 14 +/- I
< 17
< 8 13 +/- 12
< 9
< 14 12 +/- 6
< 12
< 13 13 +/- 2
< 19
< 10 14 +/- 13
<11
<17 14 +/- 8 54 +/- 13
<16-14 +/- 4 co 33 04/14/03 09122/03 MEAN' 94 04/15/03 09/24/03 MEAN*
< 319
< 161 240 +/- 223 13500 +/- 661 14900 +/- 462 14200 +/- 1980
<27
< 21 24 +/- 9
< 32
< 18 25 +/- 20
< 26
<21 23 +/- 7
< 23
< 17 20 +/- 8
< 29
< 21 25 +/- 12
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES
TABLE C-V.1 CONCENTRATIONS OF GROSS BETA IN AIR PARTICULATE SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF E-3 PCI/CU METER +/- 2 SIGMA GROUP I WEEK 1
2 3
4 5
6 7
8 9
10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 20 16 t 2 15 +/- 2 16 +/- 2 17 +/-2 19 +/-t2 19 +/-2 (1) 13 +/- 1 17 +/-2 22
- 3 18 *2 13 +/- 2 14 +/- 5 13
- 2 9
2 18 +/-2 10 +/- 2 13 +/- 2 11 +/- 2 5
2 8
2 9
2 10 +/- 2 11 +/- 2 5+/-t2 25 +/-3 20 +/- 3 15 +/-2 14 +/-3 18 +/-2 8
2 7
2 15 +/-2 17 *2 16 +/-2 10 +/-2 11
- 2 19
- 3 18 +/-3 14 *2 31 +/- 3 17 *2 15 +/- 2 20 +/-3 10 +/-3 21 +/- 2 19 +/-2 12 +/-2 12 +/- 2 9
2 18 +/-2 12 +/-2 66 16 +/- 2 17 +/-3
< 21 21 +/- 6
< 6
< 10 16
- 10 19
- 6 23 +/- 8 16 +/-8 10 +/- 3 10 +/-2 15 +/-2 8
2 13 +/- 2 6
2 12 +/- 2 11 +/- 2 4
2 7
2 9
2 7
2 9
3 5
2 21 +/- 3 19
- 3 15 +/- 2 11
- 3 18
- 3 9
2 7
2 14 +/- 3 19 +/-3 15 +/-2 9
3 10 +/- 2 17 +/-3 18 +/- 3 12 +/-2 31 +/- 3 21 +/- 3 13 +/-2 20 +/-3 10 +/-3 18 +/-2 20 +/- 3 16 +/-3 10 +/- 2 10 +/- 2 17
- 3 14 +/-3 71 14 +/- 2 15 +/- 2 15 +/- 2 17 +/- 2 16 +/- 2 16 +/- 2 9
2 14 +/- 2 18 +/- 2 22+/-3 19
- 2 12
- 2 9
2 12 +/- 2 7
2 14
- 2 8
2 14
- 2 11
- 2 4
2 10
- 2 8
2 9
2 10 +/- 2 8
2 27+/-3 2043 15 +/- 2 14 +/- 3 19 +/- 2 8
2 8
2 16 +/- 2 19 +/- 2 17 +/- 2 11
- 2 10 t 2 17 +/- 3 20+/-3 12 +/- 2 28 +/- 3 19 +/- 2 13 +/- 2 26*3 14 +/- 3 17 +/- 2 22+/-3 16
- 2 11
- 2 8
2 18
- 2 13 +/- 2 GROUP II 72-15 +/- 2 17 +/- 2 16 +/- 2 15
- 2 18
- 2 16 *2 9
2 16
- 2 18 *2 20
- 3 18
- 2 13
- 2 9
2 14 *2 8
2 18 +/-2 7
2 15 +/- 2 10 *2 4
2 9
2 9
2 8
2 10 *2 7
2 23 +/-3 20 *3 13 +/-2 13 *2 18
- 2 8
2 7
2 16
- 2 18 +/-2 15
- 2 12
- 2 9
2 18 +/- 3 17
- 3 14 *2 28 *3 20 +/-3 13 +/-2 21 +/- 3 12 *3 16
- 2 15 +/- 2 16
- 2 11 +/- 2 11
- 2 17
- 2 12
- 2 GROUP III 73 15 +/- 2 19 +/- 3 15 +/- 3 16 +/- 5 19 +/- 3 10 +/- 2 8
2 14 +/- 2 15 *2 20
- 3 15 *2 8
2 9
2 14 +/-2 11 2
15 +/-2 6
2 13 +/-2 9
2 3
2 7
2 6
3 10 +/- 2 7
2 5
2 25 +/- 3
< 2 10 +/- 2 13 +/- 3 17 +/- 2 7
2 6
2 10 +/- 3 20 +/- 3 14 +/- 2 12 +/- 2 8
2 5
2 204 3 13
- 2 28 +/-3 (1) 12 *2 24 +/- 3 12
- 2 18 +/- 2 14 +/- 2 15 i 2 11 2 9
2 17 +/-2 12 *2 14 +/- 2 4
2 17 +/-2 17 +/- 2 20 +/- 3 18 +/-2 12 +/-2 1
- 2 17 2
18 2
17 2
10 2
12 +/-2 13 +/- 2 10 +/- 2 16 +/- 2 8
2 15 +/- 2 13
- 2 5
2 7
2 9
2 9
2 8
2 6
2 23
- 3 22+/-3 14
- 2 9
2 17 +/- 2 8
2 7
2 16 +/- 2 18 +/- 2 14 +/- 2 12 +/- 2 12 +/- 2 17 +/- 3 17 +/- 2 14 *2 35 +/- 3 19 +/- 2 14 +/- 2 24 +/-3 10 +/- 2 16 +/- 2 22 +/-2 17 +/- 2 13
- 2 12 +/- 2 16 +/- 2 13 +/- 2 3
9+/-2 14 +/- 3 14 +/- 2 15 +/-2 12 +/- 2 17 +/- 2 (1) 7 1
7 2
19 +/-2 12 *2 11 +/- 2 8
2 11 +/- 2 5
2 15 +/- 2 6
2 12
- 2 11 +/- 2 4
2 6
2 10
- 2 8
2 9
2 5
2 21
- 3 21
- 3 14 +/- 2 10 +/-2 17 +/- 2 7
2 8
2 16 +/-2 17 +/- 2 16 *2 13 +/- 2 8
2 18 +/- 3 15 *2 15 +/- 2 27 +/-3 19 +/-3 13 +/- 2 23 +/-3 11 +/- 3 15 +/-2 16 +/- 2 14 +/- 2 12 +/-2 11 +/- 2 17.+/- 2 12 +/- 2 MEAN' 14 +/- 10 14 +/- 11 14 +/- 11 14
- 9 13 +/- 11 14 +/- 11 13 +/- 10 (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION
' THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES C-1 0
TABLE C-V.2 MONTHLY AND YEARLY MEAN VALUES OF GROSS BETA CONCENTRATIONS (E-3 PCI/CU. METER) IN AIR PARTICULATE SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 GROUP I - ON-SITE LOCATIONS GROUP II - INTERMEDIATE DISTANCE LOCATIONS GROUP IIl - CONTROL LOCATIONS COLLECTION PERIOD MIN. MAX.
MEAN i 2 SD*
COLLECTION PERIOD MIN.
MAX.
MEAN i 2 SD*
COLLECTION PERIOD MIN. MAX.
MEAN +/-
2 SD' 12/30UI0 02/04/03 03/04/03 03/31/03 04/28103 06/02103 06130/03 07/29/03 09/03/03 09/30/03 10/28/03 11125/03
- 02/041U3
- 03/04/03
- 03/31/03
- 04128/03
- 06/02103
- 06/30/03
- 07/29/03
- 09/03/03
- 09130/03
- 10/28/03
- 11125/03
- 12/30/03
<9 21 17 1 7
<6 19 14
- 10 10 23 16
- 10 6
18 11 *8 4
13 9 *6 5
25 12
- 15 11 20 16*6 7
19 13
- 9 9
19 14 +/- 8 12 31 19
- 16 10 21 17 i 9 9
18 13 *6 12/3U/UZ 02104/03 03/04/03 03131/03 04128/03 06/02103 06130/03 07129/03
- UZ0/4/03
- 03/04/03
- 03131/03
- 04/28/03
- 06/02/03
- 06/30/03
- 07129/03
- 09/03/03 14 19 1b +/- 3 8
18 13
- 7 8
22 14 +/- 10 8
18 11
- 8 3
15 9 +/-7 5
27 12 +/- 15
<2 20 14
- 10 6
20 13
- 10 5
20 13
- 10 12 28 18 +/- 14 12 26 18 *9 8
18 13 +/-6 12/3U/UZ 02/04/03 03/04/03 03/31/03 04/28/03 06/02/03 06130/03 07/29/03 09/03103 09130103 10128103 11125/03
- 02/04/U3
- 03/04/03
- 03/31/03
- 04/28/03
- 06/02103
- 06/30/03
- 07/29/03
- 09/03/03
- 09/30/03
- 10128/03
- 11125/03
- 12/30/03 4
2u 14t9 7
18 13 +/- 9 8
19 13 +/- 8 5
16 10
- 8 4
15 9+/- 7 5
23 11 +/- 13 9
22 16+/-9 7
18 13 +/- 10 8
18 14 +/- 6 13 35 19 +/- 15 10 24 17 +/- 10 11 17 13 +/- 5 09/03/03 - 09/30/03 09130/03 - 10/28/03 10128/03 - 11125/03 11125/03 - 12/30/03 12/30/02 - 12/30/03
<6 31 14*6 12/30/02 - 12/30/03
<2 28 14
- 5 12/30/02 - 12/30/03 4
35 14 +/-6 C,
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES
TABLE C-V.3 CONCENTRATIONS OF STRONTIUM IN AIR PARTICULATE SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF E-3 PCIICU METER *: 2 SIGMA COLLECTION STC PERIOD 3
12130/02 03131/03 03)31/03 - 06/30/03 06/30/03 - 09130103 09/30/03 - 12/30/03 Sr-89
< 1.0
< 1.1
< 9.2
< 7.8 Sr-90 c 0.2
< 0.3
<3.0
< 1.7 m
COLLECTION STC PERIOD Sr-89 Sr-90 72 12/30/02 03)31/03
< 1.1
< 0.5 03/31/03 - 06/30/03
< 1.1
< 0.3 06/30/03 - 09/30/03
< 5.1
< 1.8 09/30/03 - 12130103
< 5.1
< 2.7 MEAN' 3.1 +/- 4.6 1.3 i 2.2 73 12/30/02 03131/03
< 1.3
< 0.3 03/31/03 - 06130/03
< 1.2
< 0.3 06/30/03 - 09)30/03
< 5.3
< 1.5 09/30/03 - 12/30/03
< 7.1
< 2.6 MEAN' 4.8
- 8.7 13
- 2.6 20 12130/02 03)31/03 06/30/03 09/30/03 03/26/03
- 06/30/03
- 09130/03
- 12/30/03
< 1.3
< 1.2
< 6.0
< 9.0
< 0.2
< 0.3
<2.7
' 1.9 MEAN' 4.4
- 7.7 13 i 2.4 MEAN' 3.7 +/- 5.9 1.2 +/- 2.2 66 12130/02 03/31/03 06)30/03 09/30103 03/31/03
- 06/30/03
- 09130/03
- 12/30103
< 2.9
< 1.3
< 7.0
< 9.5
< 0.6
<0.3
<2.5
< 3.1 C
12130/02 03)31/03 03/31/03 - 06)30/03 06)30/03 - 09/30/03 09)30/03 -
12/30103
< 1.3
< 1.2
< 6.9
< 6.0
< 0.2
< 0.3
< 2.8
< 2.7 MEAN 5.2 +/- 7.6 1IS i 2.8 MEAN' 3.8 i 6.1 1.5 +/- 2.9 71 12/30102 03/31/03 06)30/03 09)30/03 03/31/03
- 06/30/03
- 09/30/03
- 12/30/03
< 1.0
< 1.1
< 5.6
< 8.1
< 0.2
<0.3
<2.0
<3.0 MEAN' 3.9 +/- 7.0 1.4 +/- 2.7
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES C-12
TABLE C-V.4 CONCENTRATION OF GAMMA EMITTERS IN AIR PARTICULATE SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF E-3 PCI/CU METER
12/30 - 03/31/03 45 2
< 0.1
< 0.1
< 0.1
< 0.1
< 0.1 03131 - 06/30103 45 6
< 0.2
< 0.3
< 0.3
< 0.2
< 0.3 06/30 - 09/30103 53 2
< 0.1
< 0.1
< 0.1
< 0.1
< 0.1 09130 - 12/30/03 50+/- 6
< 0.3
< 0.2
< 0.3
< 0.3
< 0.3 MEAN' 48+/- 8 0.2 +/- 0.1 0.2 +/- 0.1 02 0.2 0.2 +/- 0.2 0.2+/- 0.2 20 12/30 - 03/26/03 68+/- 2
< 0.1
< 0.1
<0.1
< 0.1
< 0.1 03/31 - 06130/03 42+/- 4
< 0.3
< 0.3
< 0.3
< 0.2
< 0.2 06130 - 09130103 62+/- 6
< 0.3
< 0.3
< 0.5
< 0.2
< 0.3 09/30 - 12/30/03 46+/- 5
< 0.3
< 0.4
< 0.4
< 0.3
< 0.3 MEAN' 55 +/- 25 0.2 0.2 0.3 +/- 0.2 0.3 +/- 0.4 0.2 +/- 0.2 0.2 +/- 0.2 66 12130 - 03/31/03 48 +/- 8
< 0.5
< 0.6
< 0.5
< 0.4
< 0.4 03131 - 06130/03 46 +/- 5
< 0.2
< 0.2
< 0.4
< 0.1
< 0.2 06/30 - 09/30/03 51 +/- 9
< 0.4
< 0.4
< 0.3
< 0.4
< 0.4 09/30 - 12130/03 49+/- 7
<0.4
< 0.3
< 0.4
< 0.3
< 0.3 MEAN 48 +/- 4 0.4 +/- 0.3 0.4 +/- 0.3 0.4 +/- 0.2 0.3 +/- 0.2 0.3 +/- 0.2 71 12/30 - 03131/03 51 +/- 2
< 0.1
< 0.09
< 0.2
< 0.07
< 0.07 03131 - 06/30/03 44 +/- 5
< 0.3
< 0.4
< 0.3
< 0.2
< 0.2 06/30 - 09130/03 59 +/- 7
< 0.4
< 0.4
< 0.4
< 0.3
< 0.4 09/30 - 12/30/03 44 +/- 4 0.2
< 0.2
< 0.3
< 0.2
< 0.3 MEAN' 49 +/- 14 0.3 0.3 0.3 +/- 0.3 0.3 +/- 0.2 0.2 0.2 0.2 +/- 0.2 72 12/30 - 03131103 60 +/- 2
< 0.1
< 0.2
< 0.1
<0.1
< 0.1 03131 - 06130103 47 +/- 5
< 0.3
< 0.3
< 0.3
< 0.3
< 0.3 06/30 - 09130/03 57 6
< 0.4
< 0.5
< 0.5
< 0.3
< 0.4 09/30 - 12/30/03 45 5
< 0.2
< 0.3
< 0.2
< 0.2
< 0.2 MEAN' 52 15 0.3 +/- 0.2 0.3 +/- 0.3 0.3 +/- 0.3 0.2 +/- 0.2 0.3 +/- 0.2 73 12/30 - 03/31/03 41 3
< 0.2
< 0.2
< 0.2
< 0.2
< 0.2 03131 - 06/30/03 45 5
< 0.2
< 0.2
< 0.2
< 0.2
< 0.2 06130 - 09130/03 39 6
< 0.4
< 0.4
< 0.4
< 0.3
< 0.3 09130 - 12/30/03 44 6
< 0.4
< 0.4
< 0.2
< 0.2
< 0.4 MEAN*
42 5
0.3 +/- 0.2 0.3 +/- 0.2 02 +/- 0.2 0.2 0.2 0.3 +/- 0.2 C
12/30 - 03/31/03 53 +/- 2
< 0.07
< 0.09
< 0.08
<0.1
< 0.08 03/31 - 06130/03 41 5
< 0.3
< 0.3
< 0.3
< 0.2
< 0.3 06/30 - 09130/03 54 +/- 2
< 0.08
< 0.09
< 0.2
< 0.06
< 0.08 09130 - 12/30/03 48 +/- 5
< 0.3
< 02
< 0.4
< 0.3
< 0.3 MEAN' 49 +/- 12 02 +/- 0.2 0.2 +/- 0.2 02 +/- 0.3 0.1 +/- 0.2 0.2 +/- 0.3
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES C-13
TABLE C-VI.1 CONCENTRATIONS OF 1-131 IN AIR IODINE SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF E-3 PCI/CU METER +/- 2 SIGMA GROUP I GROUP II GROUP Ill WEEK 20 66 71 72 73 C
3 1
'6
<7
'4
<4
<5
<6
<6 2
'4
<5
'2
<2
<3
'4
'6 3
<6
<32
<7
<7
<10
<5
<6 4
< 5 6
<4
<4
<11
<4
< 5 5
<2
<7
<2
<2
<2
<3
<3 6
<4
<18
<3
<3
<3
<3
<4 7
(1)
< 22
< 5
< 5
< 5
< 5 (1) 8
<2
<31
<3
<3
<4
<5
<3 9
<5
<15
<5
<5
<5
<5
<5 10
<3
<16
<4
<4
<5
<4
<3 11
<5
<26
<7
<7
<8
<5
<5 12
<9
<8
<5
<5
<6
<8
<9 13
<15
<4
<3
<3
<3
<3
<3 14
<2
<2
<4
<4
<4
<2
<2 15
<5
<5
<2
<2
<2
<4
<5 16
<4
<4
<4
<4
<4
<3
<3 17
<4
<4
<3
<3
<3
<4
<4 18
<6
<7
<4
<4
<4
<5
<6 19
<4
<5
<4
<4
<4
<4
<4 20
<3
<4
<4
<4
<4
<3
<3 21
<3
<3
<3
<3
<3
<2
<3 22
<5
<3
< 3
<3
<5
<5
<6 23
<4
<4
<4
<4
<4
<3
<4 24
<4
<5
<4
<4
<4
<4
<4 25
<4
<4
<4
<4
<4
<4
<4 26
<6
<7
<6
<5
<6
<4
'5 27
<7
<8
<7
<4
<6
<4
<5 28
<4
<5
<4
<3
<4
<3
<4 29
< 18
<11
< 18
< 19
< 21
< 13
< 13 30
<4
<5
<4
<7
<4
<6
<7 31
<3
<3
<2
<9
<2
<9
<9 32
<5
<6
<5
<4
<5
<4
<4 33
<3
<3
<3
<4
<4
<4
<4 34
<9
<7
<6
<9
<8
< 8
<9 35
<5
<2
<4
<3
<4
<3
<2 36
<6
<7
<6
<6
<6
<6
<6 37
<2
<3
<3
<2
<3
<4
<2 38
<7
<7
<6
<6
<6
<6
<7 39
<2 1
<2
<1
<2
<1
<2 40
<6
<7
<6
<5
<6
<5
<6 41
< 10
<9
< 8
< 10
< 8
< 9
< 10 42
<9
<11
<9
<7 (1)
<6
<7 43
<5
<6
<5
<5
<5
<4
<5 44
<7
<8
<7
<7
<7
<6
<7 45
<6
<7
<6
<7
<6
<6
<7 46
<5
<5
<4
<4
<4
<4
<4 47
<9
< 10
< 9
<9
< 8
< 8
<9 48
<8
<9
<7
<8
<7
<8
<9 49
<6
<7
<6
<7
<6
<7
<7 50
<2
<3
<2
<3
<2
<2
<3 51
<7
<8
<6
<8
<6
<8
<8 52
<8
<7
<6
<8
<6
<8
<8 MEAN' 6 6 8 +/- 13 5 +/- 5 5 +/-6 5+/-6 5 +/- 4 5 +/- 5 (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION
TABLE C-VII.1 CONCENTRATIONS OF STRONTIUM AND GAMMA EMITTERS IN VEGETATION SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF PCI/KG WET +/- 2 SIGMA STC 35 Cabbage 35 Collards 35 Cabbage c
35
'-a Collards 35 Collards 35 Kale COLLECTION PERIOD 08/28/03 08/28/03 09/18103 09118/03 10/24103 10/24/03 MEAN*
Sr-89
<8
< 9
< 15
<7
<6
< 19 11 +/- 10 Sr-90
<3
<3 16
- 4
<3 12 +/- 1 14 +/- 2 8 +/- 12 K-40 3550 +/- 296 3280 +/- 180 2420 +/- 420 1590 +/- 399 2710 +/- 111 3620 +/- 101 2862 +/- 1564 1-131
< 38
< 30
<33
< 37
< 59
< 43 40 +/- 20 Cs-134
<8
<6
<21
< 20
<4
< 2 10 +/- 16 Cs-137 18
- 9 15 +/- 7
<26
< 28.
16 +/- 4 20 +/- 5 20 +/- 11 Ba-140
<76
<56
< 102
< 105
<77
< 51 78 +/- 45 La-140
< 25
< 18
<30
< 34
< 25
< 16 24 +/- 14
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES
TABLE C-VII.1 CONCENTRATIONS OF STRONTIUM AND GAMMA EMITTERS IN VEGETATION SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF PCI/KG WET +/- 2 SIGMA STC 36 Cabbage 36 Tomatoes 36 Collards 36 Tomatoes 0) 36 Collards 36 Kale 36 Tomatoes COLLECTION PERIOD 08/28/03 08/28/03 09316103 09/18103 10/24/03 10/24/03 10/24/03 MEAN*
Sr-89 Sr-90
< 12
< 10
<8
< 10
< 11
< 18
< 20 12 +/- 9 4 *2
<3 8 *2
<2 15 +/- 2 16 +/- 3
<2 7 +/- 12 K-40 1950 +/- 190 2070 i 190 3420 +/- 468 2200 +/- 206 4120 +/- 178 4630 +/- 163 2520 +/- 103 2987 +/- 2149 1-131
< 40
< 40
<32
< 13
< 57
< 60
< 51 42 +/- 32 Cs-134
<8
< 9
< 18
< 9
< 4
< 4
< 4 8 +/- 10 Cs-137
< 10
< 9
<22
< 11
<5
<5
< 4 9 +/- 12 Ba-140
<77
<77
<99
< 40
<82
< 79
<70 75 +/- 35 La-140
< 31
< 27
<29
< 13
<22
< 18
<20 23 +/- 13
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES
TABLE C-VII.1 CONCENTRATIONS OF STRONTIUM AND GAMMA EMITTERS IN VEGETATION SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF PCI/KG WET +/- 2 SIGMA STC COLLECTION PERIOD Sr-89 Sr-90 K-40 1.131 Cs-134 Cs-137 Ba-140 La-140 SSE Sedor" Rhubarb SSE Sedor" Tomatoes 08/28/03 08128/03
<6 4 *2
<10 5 +/-2 3950 +/- 151
< 28
<6 28 +/-6
< 54
< 87
< 18
< 29 2240 +/- 229
< 10
< 12 SSE Sedtor 09/18103 Rhubarb
<7 6 *3 3300
- 401
< 30
< 18
< 24
< 93
< 26 0
-J SSE Sedor" Tomatoes 09118103
<7
<3 2210 *268
< 17
< 12
< 50
< 12 SSE Sedor-10/24/03 Rhubarb
<16 11 *3 4470
- 126
< 60
<4 14 *4
< 84
< 25 MEAN*
9 +/-8 6 *6 3234 +/- 2020 36 +/- 33 9
- 11 18 +/- 15 74 +/- 40 22 +/- 14
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES
- THE GARDEN AT STATION 66 FAILED DUE TO EXCESSIVE AND PERSISTENT RAINFALL IN THE SPRING OF 2003. VEGETABLES FROM A GARDEN IN THE SSE SECTOR WERE SUBSTITUTED.
TABLE C-VIII.1 QUARTERLY TLD RESULTS FOR OYSTER CREEK GENERATION STATION, 203 RESULTS IN UNITS OF MILLI-ROENTGEN/STD. QUARTER +/- 2 STANDARD DEVtATIONS STATION CODE C
14 1
TI 3
4 S
6 8
9 it 22 46 47 48 51 52 53 54 55 56 57 58 59 61 62 63 64 65 66 68 71 72 73 74 75 78 79 81 82 84 85 86 88 89 90 92 98 99 MEAN
+/- 2S.D.
13.2 +/- 4.3 15.7 +/- 3.5 14.6 +/- 2.8 14.4 +/- 42 12.8 +/- 5.0 11.9 +/- 4.8 17.7 +/- 2.3 13.5 +/- 5.6 13.8 +/- 4.1 14.2 +/- 5.2 13.3 +/- 5.5 12.0 +/- 4.7 11.1 +/- 1.8 13.0 +/- 2.7 12.5 3.7 16.6 +/- 52 15.8 +/- 5.0 15.4 +/- 4.8 13.1 +/- 3.5 18.9 +/- 4.0 17.7 +/- 3.8 14.3 +/- 4.8 14.5 +/- 52 14.2 +/- 43 13.4 +/- 4.6 14.6 +/- 5.0 14.0 +/- 4.0 13.8 +/- 4.3 14.7 +/- 3.8 13.3 +/- 3.1 14.3 7.7 13.6 +/- 4.0 14.8 +/- 5.7 13.5 6.3 12.7 +/- 3.5 13.8 +/- 3.9 11.9 +/- 2.6 13.6 +/- 4.7 12.5 i 6.0 13.8 +/- 4.5 14.6 +/- 4.3 12.5-F 4.1 13.7 +/- 5.8 10.8 i 3.4 12.0 +/- 3.6 11.8 +/- 3.6 14.1 +/- 4.8 14.2 +/- 4.6 13.3 4.7 JAN - MAR APR - JUN JUL - SEP OCT - DEC 12.3 +/- 3.4 16.5 1.9 15.4 +/- 2.3 13.1 +/- 2.1 14.0 4.1 16.7 2.4 14.5 3.9 15.5 0.9 15.3 4.3 11.1 +/- 1.1 17.1 +/- 1.4 14.6 +/- 1.6 14.1 i 4.0 13.6 +/- 1.3 18.9 +/- 1.3 16.7 +/- 3.6 13.0 +/- 4.0 14.0 +/- 1.5 12.7 +/- 1.3 12.9 +/- 0.9 12.2 +/- 1.6 12.8 +/- 2.3 (I) 14.9
- 10.1 12.5 I 1.6 (1) 14.3 +/- 4.1 11.5 +/- 1.5 16.1 +/- 4.0 12.3 +/- 4.5 13.2
- 0.1 13.0 +/- 2.5 15.0 +/- 3.0 15.0
- 1.9 13.8 +/- 0.8 15.8 t 1.8 13.4 +/- 0.6 16.4 +/- 0.9 12.3 +/- 1.7 11.0
- 2.4 12.5
- 0.8 15.2 +/- 1.7 15.3
- 2.8 14.7
- 4.4 10.9 +/- 1.5 13.2 +/-0.6 12.7 +/- 1.3 12.3 +/- 1.7 9.4 +/- 0.5 10.0 +/- 1.1 11.0 +/- 1.9 10.7 +/- 1.8 9.5 +/- 0.5 9.5 +/- 1.0 12.9 +/- 1.8 13.4 +/- 1.9 13.1 +/- 1.0 10.9 +/- 1.6 16.6 +/- 1.3 15.6 +/- 3.4 11.8 +/- 1.4 12.2 +/- 1.0 12.2 +/- 1.4 10.9 +/- 1.0 12.0 +/- 0.7 12.1 +/- 0.9 11.7 +/- 0.8 12.0 +/- 0.9 11.6 +/- 2.2 10.1 +/- 1.2 11.3 +/- 0.9 17.3 +/- 3.6 8.9 +/- 0.8 10.8 +/- 0.6 11.6+/- 1.1 10.5 +/- 1.8 10.2 +/- 0.3 9.2 +/- 1.2 10.9 +/- 1.2 11.4 +/- 1.4 9.6 +/- 1.0 9.6 +/- 0.8 9.0 +/- 1.0 10.2 +/- 0.9 9.4 +/- 0.8 10.6 +/- 1.7 11.0 +/- 0.6 9.8 +/- 0.4 13.5 +/- 0.6 15.8 +/- 1.2 14.4 +/- 1.6 15.2 +/- 0.6 12.7 +/- 1.8 13.6 +/- 1.4 18.5 +/- 1.5 13.0 +/- 1.3 13.8 +/- 0.9 14.0 +/- 1.7 13.1 +/- 1.4 12.4 +/- 0.7 11.7 +/- 1.6 13.9 +/- 1.6 13.8 +/- 1.0 17.5 +/- 1.7 16.0 +/- 2.1 16.0 +/- 1.1 12.6 +/- 0.9 18.4 +/- 1.4 18.6 +/- 1.6 15.1 +/- 1.5 14.1 +/- 1.3 14.9 +/- 0.7 13.2 +/- 1.2 14.8 +/- 1.5 14.6 +/- 28 13.8 +/-1.2 15.2 +/- 0.6 13.8 +/- 1.7 15.2 +/- 1.1 15.1 +/- 2.1 13.2 +/- 1.9 14.3 +/- 3.4 12.5 +/- 1.3 14.2 +/- 2.6 12.2 +/- 0.9 13.9 +/- 2.5 13.3 +/- 1.1 14.3 +/- 0.9 15.0 +/- 2.5 12.6 +/- 1.4 14.1 +/- 1.3 11.2 +/- 2.8 12.4 +/- 2.1 11.8 +/- 0.9 14.6 +/- 0.9 14.3 +/- 1.3 13.7 +/- 2.4 16.0 +/- 1.5 17.2 +/- 1.1 15.8 +/- 1.5 17.0 +/- 1.1 15.2 +/- 1.2 10.2 +/- 0.8 16.9 +/- 1.5 14.2 +/- 0.6 15.8 +/- 1.5 16.7 +/- 1.9 15.4 +/- 0.6 15.0 +/- 0.5 10.4 +/- 0.5 12.0 +/- 1.0 112 +/- 0.8 18.9 +/- 1.6 19.2 +/- 1.2 18.5 +/- 1.0 15.1 +/- 0.8 21.5 +/- 1.9 19.8 +/- 1.5 17.2 +/- 1.5 17.3 +/- 1.5 16.9 +/- 0.9 16.5 +/- 1.3 17.0 +/- 1.5 16.6 +/- 1.3 16.0 +/- 1.9 16.5+/- 1.4 15.1 +/- 0.8 17.7 +/- 0.9 16.8 +/- 0.8 17.0 +/- 1.7 14.6 +/- 1.0 15.0 +/- 0.8 16.3 +/- 2.3 (1) 15.4 +/- 1.7 15.5 +/- 1.1 16.3 +/- 1.1 16.0 +/- 1.0 14.4 +/- 12 14.8 +/- 0.8 (1) 14.3 +/- 1.5 13.6 +/- 0.4 15.9 +/- 0.8 16.3 +/- 0.9 14.8 +/- 1.2 (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-18
TABLE C-VIII.2 MEAN QUARTERLY TLD RESULTS FOR THE SITE BOUNDARY, MIDDLE, SPECIAL INTEREST AND CONTROL LOCATIONS FOR OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF MILLI-ROENTGEN PER STD. QUARTER +/- 2 STANDARD DEVIATIONS OF THE STATION DATA STATION CODE SITE BOUNDARY
+/- 2 S. D.
MIDDLE SPECIAL INTEREST CONTROL JAN-MAR APR-JUN JUL-SEP OCT-DEC 14.4 +/- 3.9 12.6 +/- 3.1 15.2 +/- 3.5 17.4 +/- 3.5 14.3 +/- 3.4 10.3 +/- 1.7 14.1 +/-2.8 14.8 +/- 4.1 13.9 +/- 3.3 10.7 +/- 4.2 13.2 +/- 2.4 15.2 +/- 3.6 14.4 +/- 5.9 12.1 +/- 3.3 14.7 +/- 3.3 16.6 +/- 1.7 TABLE C-VIII.3
SUMMARY
OF THE AMBIENT DOSIMETRY PROGRAM FOR OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF MILLI-ROENTGEN/STD. QUARTER LOCATION SITE BOUNDARY MIDDLE DISTANCE SPECIAL INTEREST CONTROL SAMPLES ANALYZED 63 55 56 8
PERIOD MINIMUM 10.9 8.9 9.0 10.9 PERIOD MAXIMUM 21.5 18.5 17.3 17.2 PERIOD MEAN
- 2 s.d.
14.9 +/- 4.9 13.5 +/- 4.7 13.2 +/- 4.6 14.4 +/- 4.5 SITE BOUNDARY STATIONS -1,51,52,53,54,55,56,57,58,59,61,62,63,64,65,66 INTERMEDIATE DISTANCE STATIONS - 4,5,22,47,48,68,73,74,75,79,82,84,85,86,98,99 SPECIAL INTEREST STATIONS - 3,6,8. 9,11,46,71,72,78,81, 88,89,90,92, T1 CONTROL STATIONS - C, 14 C-19
TABLE C-IX.1
SUMMARY
OF COLLECTION DATES FOR SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 SURFACE WATER (TRMUM LIQUID SCINTILLATION)
COLLECTION PERIOD JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC 04 23 24 33 94 01/08103 01108/03 02106103 02106/03 03/13103 03/13103 1/15/03 04/14103 04102103 04102103 05102/03 05102103 06104103 06104103 07/07/03 07/07103 08/05/03 08/05103
/12313 09/22103 09103103 09103103 10107103 10107/03 11104103 11104103 12102/03 12102103 SURFACE WATER (GAMMA SPECTROSCOPY)
COLLECTION PERIOD JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC 23 24 33 01108103 02106103 03/13103 04/15103 04/14103 04102103 05102103 06104/03 07107/03 08105103 09/23103 09/22103 09103103 10107/03 11/04103 12/02/03 94 01/08103 02106103 03/13/03 04102103 05102103 06104103 07107103 08/05/03 09103103 10/07/03 11/04103 12102103 WELL WATER (TRITIUM & GAMMA SPECTROSCOPY)
COLLECTION PERIOD 1
37 JAN-MAR APR-JUN JUL-SEP OCT-DEC 12111102 - 02114103 12111102 - 02/14103 03/13/03 - 05107103 03/25103 - 05107103 07/02103 - 09116103 07/02103 - 09/16103 11/07103 - 12119103 11107103 - 12V19/03 38 12/111/02 - 02/14/03 03/25/03 - 05107/03 07102103 - 09116/03 11/07103 - 12/19103 0
AIR PARTICULATE (GAMMA SPECTROSCOPY)
COLLECTION PERIOD C
3 20 66 JAN-MAR APR-JUN JUL-SEP OCT-DEC 12/30102 - 03/31/03 12/3002 - 03131103 03131/03 - 06/30103 03/31103 - 06/30103 06130/03 - 09130103 06130103 - 09130103 09/30103 - 12/30103 09130103 - 12/30/03 12/30102 - 03/31103 12/30/02 - 03/31/03 03131103 - 06130/03 03131103 - 06130103 06130103 - 09/30103 06/30/03 - 09130103 09130/03 - 12130103 09/30103 - 12130103 COLLECTION PERIOD 71 72 73 JAN-MAR APR-JUN JUL-SEP OCT-DEC 12/30102 - 03/31103 12130102 - 03/31103 03/31103 - 06/30/03 03131/03 - 06/30103 06/30103 - 09130/03 06130103 - 09130103 09/30103 - 12/30/03 09130/03 - 12/30103 12/30/02 - 03/31103 03131/03 - 06130103 06130/03 - 09130103 09/30/03 - 12130103 C-20
TABLE C-X.1
SUMMARY
OF COLLECTION DATES FOR SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 AIR PARTICULATE (GROSS BETA & 1-1 31)
COLLECTION PERIOD C
3 20 66 71 1
12130102 - 01/06103 2
01/06t03 - 01113/03 3
01/13103 - 01/20/03 4
01/20103 - 01/27/03 5
01127/03 - 0204/03 6
02/04/03 - 0211103 7
02111/03 - 0218/03 8
02118/03 - 0224/03 9
02/24/03 - 03103/03 10 03/03/03 - 03/10/03 11 03/10/03 - 03117/03 12 03/17/03 - 03/24/03 13 03124/03 - 03131/03 14 03131/03 - 04107/03 15 04/07/03 - 04114/03 16 04/14103 - 04121/03 17 04/21/03 - 04128/03 18 04128103 - 05/05/03 19 05/05103 - 05/12103 20 05/1203 - 05/19/03 21 05/19/03 - 05126/03 22 05126/03 - 06/02103 23 06/02/03 - 06/09/03 24 06/09/03 - 06/16/03 25 06/1603 - 06123/03 26 06123/03 - 06/30/03 27 06/30/03 - 07/07/03 28 07/07/03 - 07/15/03 29 07)15/03 - 07/21/03 30 07/21/03 - 07/29/03 31 07129/03 - 08/05/03 32 08/05/03 - 08/12103 33 08/12/03 - 08/19/03 34 08/19/03 - 08126/03 35 08126/03 - 09/03/03 36 09/03/03 - 09/09/03 37 09/9/03 - 09/16/03 38 09/16/03 - 09/23/03 39 09123103 - 09130/03 40 09/30/03 - 10/07/03 41 10/07/03 - 10/14/03 42 10/14/03 - 10/21/03 43 10121103 - 10/28/03 44 10/28/03 - 11/04/03 45 11/04/03 - 11/11/03 46 11/11/03 - 11/18/03 47 11118/03 - 11125/03 48 11/25/03 - 12/02103 49 1202/03 - 12/09/03 50 12109/03 - 12/16/03 51 12/16/03 - 12/23/03 52 12V23/03 - 12/30/03 12/30/02 - 01/06/03 01/06/03 - 01/11/03 01/13/03 - 01/20/03 01120/03 - 01/27/03 01127/03 - 02104103 02/04/03 - 0211/03 (1) 02/11/03 - 02124103 02124/03 - 03/03103 03/03103 - 03/10/03 03/10103 - 03/17/03 03/17/03 - 03124/03 03124/03 - 03/31103 03/31/03 - 04107/03 04/07/03 - 04/14/03 04/14/03 - 04121/03 04/21/03 - 04128103 04/28/03 - 05/05/03 05/05/03 - 05/1203 05/12/03 - 05/19/03 05/19/03 - 05126/03 05/26/03 - 0610203 06/02103 - 06/09/03 06/09/03 - 0616/03 06/16/03 - 06/23/03 06123/03 - 06130/03 06130/03 - 07/07/03 07/07/03 - 07/15/03 07/15/03 - 07/21/03 07121/03 - 07129/03 07129/03 - 08/05/03 08/05103 - 08/12/03 08/12/03 - 08/19/03 08/19/03 - 08126/03 08/26/03 - 09/03/03 09/03103 - 09/09/03 09/09103 - 09/16/03 09/16/03 - 09123/03 09123103 - 09/30/03 09130/03 - 10/07/03 10/07103 - 10/14/03 10/14/03 - 10/21103 10121103 - 10128103 10/28/03 - 11/04/03 11/04/03 - 11/11/03 11/11/03 - 11/18/03 11/18103 - 11/25103 11125/03 - 12102103 12102/03 - 12109/03 12/09/03 - 1216/03 12116103 - 1223/03 12123/03 - 1230/03 12/30/02 - 01/06103 01/06/03 - 01/13/03 01/13/03 - 01120/03 01120/03 - 01127/03 01/27103 - 02104/03 02V04/03 - 0211/03 (1) 02/11/03 - 02/25103 02125/03 - 03/04/03 03/04/03 - 03/10/03 03/10/03 - 03/17/03 03/17/03 - 03/24/03 03124/03 - 03/26/03 03/31/03 - 03/26/03 04/07t03 - 03126/03 04/14/03 - 03/26/03 04/21103 - 03/26/03 04/28/03 - 03/26/03 05/05/03 - 03126/03 05/12/03 - 03/26/03 05/19/03 - 03/26/03 05/26103 - 03/26/03 06/02/03 - 03/26/03 06/09/03 - 03/26/03 06/16/03 - 03/26/03 06/23103 - 03/26/03 06/30103 - 04/02/03 07/07t03 - 07/15/03 07/15t03 - 07/21/03 07121103 - 07129/03 07129/03 - 08/05/03 08/05103 - 08/12/03 08/12103 - 08/19/03 08/19/03 - 08126/03 08126/03 - 09/03/03 09/03103 - 09/09/03 09/09/03 - 09/16/03 09/16t03 - 09123/03 09123/03 - 09/30/03 09/30103 - 10/07/03 10/07103 - 03126/03 10/14/03 - 03/26/03 10/21103 - 03126/03 10128103 - 03/26/03 11/04/03 - 03126103 11/11103 - 03126/03 11/18/03 - 03/26/03 11t25/03 - 03/26/03 12/02/03 - 03126/03 12/09103 - 03/26/03 12V16/03 - 03126103 12123103 - 03126103 12/30/02 - 01/06/03 12130/02 - 01/06/03 01/06/03 - 01113/03 01/06/03 - 01/13/03 01/13/03 - 01/15/03 01113/03 - 01120/03 01123/03 - 01125/03 01120/03 - 01/27/03 01/27/03 - 0204/03 01/27/03 - 0204/03 02/04/03 - 02/05/03 02/04/03 - 0211/03 02/13/03 - 0218103 02111/03 - 0218/03 02121/03 - 02125/03 02118/03 - 02/25/03 02125/03 - 03/04/03 02125/03 - 03104/03 03/04/03 - 03110/03 03/04/03 - 03/10/03 03/10/03 - 03/17103 03/10/03 - 03/17/03 03/19/03 - 03/24/03 03/17)03 - 03/24103 03124/03 - 03131103 03124103 - 03131/03 03/24103 - 04/07/03 03131/03 - 04/07/03 03124103 - 04/14/03 04/07)03 - 04/14/03 03124/03 - 04/21/03 04/14/03 - 04121/03 03124103 - 04128103 04121/03 - 04128/03 03124103 - 05/05/03 04128/03 - 05/05/03 03124/03 - 05/12103 05/05/03 - 05/12103 03124/03 - 05/19/03 05112/03 - 05/19/03 03124/03 - 05126/03 05/19/03 - 05126/03 03124/03 - 06/02/03 05/26/03 - 06/0203 03124/03 - 06/09/03 W02103 - 06/09/03 03124/03 - 06)16/03 06/09/03 - 06/16/03 03124/03 - 06/23103 06/16/03 - 06/23/03 03124/03 - 06130103 06/23/03 - 06/30/03 03/31/03 - 07/07103 W30/03 - 07/07t03 04/07/03 - 07/15/03 07/07/03 - 07)15/03 07/15/03 - 07/21)03 07/15/03 - 07/21103 07121/03 - 07129/03 07121/03 - 07129103 07/29/03 - 08/05/03 07/29/03 - 08/05/03 08105/03 - 08/12/03 08/05/03 - 08)1203 08/12/03 - 08119/03 08/12/03 - 08/19/03 08/19/03 - 08126/03 08/19/03 - 08126/03 08126/03 - 09/03/03 08126103 - 09/03/03 09/03/03 - 09/09/03 09103)03 - 09/09/03 09/09/03 - 09/16103 09/09/03 - 09/16/03 09/16/03 - 09/23/03 09/16/03 - 09/23/03 09123/03 - 09130/03 09/23/03 - 09/30/03 09/30/03 - 10/07/03 09/30)03 - 10107103 03124/03 - 10/14/03 10/07/03 - 10/14/03 03124/03 - 10121/03 10/14/03 - 10121/03 03/24/03 - 10128/03 10/21/03 - 10/28/03 03124/03 - 11)04/03 10/28/03 - 11/04/03 03124/03 - 11/11/03 11/04103 - 11/11/03 03/24/03 - 11/18/03 11/11)03 - 11/18/03 03124/03 - 11125/03 11)18/03 - 11125103 03124103-12102/03 11/25/03 - 12/02/03 03124103 - 1209/03 12/02/03 - 12/09/03 03124/03 - 1216/03 12/09/03 - 12/16t03 03124103 - 1223/03 12116103 - 12123t03 03124103 - 12/30/03 12123103 - 1230/03 (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION.
C-21
TABLE C-IX.1
SUMMARY
OF COLLECTION DATES FOR SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 AIR PARTICULATE (GROSS BETA & 1-131)
COLLECTION PERIOD 1.
2 3
4 5
6 7
8 9
10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 72 73 12/30/02 - 01/06103 01106103 - 01/13/03 01/13/03 - 01/20/03 01/20/03 - 01/27/03 01/27103 - 02/04103 02/04/03 - 02/11/03 02/11/03 - 02/18/03 02)18/03 - 02/25/03 02/25/03 - 03/04/03 03/04/03 - 03/10/03 03/10/03 - 03/17/03 03/17103 - 03124103 03124/03 - 03/31/03 03/31/03 - 04/07/03 04/07103 - 04/14/03 04/14/03 - 04121/03 04/21/03 - 04/28/03 04/28/03 - 05/05/03 05/05/03 - 05/12/03 05/12/03 - 05/19/03 05/19/03 - 05126/03 05/26/03 - 06/02/03 06/02/03 - 06/09/03 06/09/03 - 06/16103 06/16/03 - 06/23/03 06/23/03 - 06/30/03 06/30/03 - 07/07/03 07/07/03 - 07/15/03 07/15/03 - 07/21/03 07/21/03 - 07/29/03 07/29/03 - 08/05/03 08/05/03 - 08/12/03 08/12/03 - 08/19/03 08/19/03 - 08/26/03 08/26/03 - 09/03/03 09/03/03 - 09/09/03 09/09/03 - 09/16/03 09/16/03 - 09/23/03 09/23/03 - 09/30/03 09/30/03 - 10/07/03 10/07/03 - 10/14/03 10/14/03 - 10/21/03 10121/03 - 10/28/03 10/28/03 - 11/04/03 11/04/03 - 11111/03 11111103 - 11/18/03 11/18/03 - 11/25/03 11/25/03 - 12/02/03 12/02/03 - 12/09/03 12/09/03 - 12/16/03 12/16/03 - 12/23/03 12123/03 - 12/30/03 12/30/02 - 01/06/03 01/06/03 - 01/13/03 01/13/03 - 01120/03 01124/03 - 01/7/03 01/27/03 - 02104/03 02/04/03 - 02/11/03 02/11/03 - 02/18/03 02/18/03 - 02125/03 02/25/03 -03/04/03 03/04/03 - 03110103 03/10/03 - 03117103 03117/03 - 03/24103 03/24/03 - 03/31/03 03/31/03 - 04/07/03 04/07/03 - 04/14/03 04/14/03 - 04/21/03 04121/03 - 0428/03 04128/03 - 05/05/03 05/05/03 - 05/12/03 05/12/03 - 05/19/03 05/19/03 - 05/26103 05/26/03 - 06/02/03 06/02/03 - 06/09/03 06/09/03 - 06/16/03 06/16/03 - 06/23/03 06/23/03 - 06/30/03 06/30/03 - 07107/03 07/07/03 - 07115/03 07115/03 - 07/21103 07121/03 - 07129/03 07129/03 - 08/05/03 08/05/03 - 08112/03 08/12/03 - 08/19/03 08/19/03 - 08126103 08/26/03 - 09/03/03 09/03/03 - 09/09/03 09/09/03 - 09/16/03 09/16/03 - 09/23/03 09/23/03 - 09/30/03 09/30/03 - 10/07/03 10/07/03 - 10114/03 10/14/03 - 10/21/03 10/21/03 - 1028/03 10/28/03 - 11/04/03 11104/03 - 11111/03 11/11103 - 11118/03 11/18/03 - 11125/03 11125/03 - 12/02/03 12/02103 - 12109/03 12/09/03 - 12/16/03 12/16/03 - 12/23/03 12123/03 - 12/30/03 C-22
TABLE C4X.1
SUMMARY
OF COLLECTION DATES FOR SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 TLD STATION CODE C
14 1
T1 3
6 8
9 11 22 51 52 53 54 55 56 57 58 59 61 62 63 64 65 66 68 71 72 73 74 75 78 79 81 82 84 85 86 88 89 90 92 98 99 JAN - MAR APR - JUN JUL - SEP OCT - DEC 01113103 - 04/14103 01/13103 - 04/14103 01113103 - 04/14/03 01/13103 - 04/14/03 01113103 - 04114/03 01113103 - 04114/03 01113103 - 04114/03 01113103 - 04114/03 01/13103 - 04114/03 01/13103 - 04/14/03 01/13103 - 04/14103 01113103 - 04/14103 01113103 - 04/14/03 01113103 - 04114103 01/13103 - 04/14/03 01/13103 - 04/14103 01/13103 - 04/14/03 01/13103 - 04/14/03 01/13103 - 04/14/03 01113/03 - 04/14/03 01113103 - 04114103 01/13103 - 04/14/03 01/13/03 - 04/14/03 01/13/03 - 04114/03 01/13/03 - 04/14/03 01/13103 - 04/14103 01/13/03 - 04/14/03 01/13103 - 04/14/03 01/13103 - 04/14/03 01/13103 - 04114/03 01/13103 - 04114103 01/13/03 - 04114/03 01/13/03 - 04/14/03 01/13103 - 04114/03 01/13103 - 04/14/03 01/13103 - 04/14103 01/13103 - 04/14/03 01/13103 - 04/14/03 01113103 - 04/14/03 01113103 - 04/14/03 01113103 - 04/14/03 01113103 - 04/14/03 01113103 - 04/14/03 01113103 - 04/14/03 04/14/03 - 07/14103 04/14/03 - 07/14103 04/14/03 - 07114103 04/14103 - 07/14103 04/14103 - 07/14/03 04/14103 - 07/14103 04/14/03 - 07114103 04/14103 - 07114/03 04/14/03 - 07114/03 04/14/03 - 07/14/03 04114/03 - 07/14/03 04/14/03 - 07/14/03 04114103 - 07/14/03 04/14103 - 07/14/03 04/14/03 - 07)14103 04/14/03 - 07114/03 04/14/03 - 07/14/03 04114103 - 07114/03 04/14103 - 07114103 04114/03 - 07/14/03 04/14/03 - 07/14103 04114/03 - 07114/03 04114/03 - 07/14103 04/14103 - 07/14/03 04/14103 - 07/14/03 04/14/03 - 07114103 04114/03 - 07/14103 04/14103 - 07/14/03 04/14103 - 07/14103 04/14103 - 07/14103 04/14103 - 07/14/03 04/14103 - 07/14103 04114/03 - 07/14/03 04114/03 - 07/14103 04114/03 - 07/14103 04/14103 - 07/14/03 04/14/03 - 07/14103 04114/03 - 07/14103 04/14/03 - 07/14/03 04/14/03 - 07/14/03 04/14/03 - 07114/03 04/14/03 - 07/14/03 04/14/03 - 07/14/03 04/14/03 - 07/14/03 07/14/03 - 10/13103 07114/03 - 10113103 07114/03 - 10113103 07/14103 - 10113103 07/14103 - 10113103 07114103 - 10113103 07/14103 - 10/13/03 07/14/03 - 10/13103 07/14/03 - 10113103 07/14/03 - 10/13103 07114/03 - 10113103 07/14/03 - 10/13103 07114/03 - 10113103 07/14/03 - 10/13103 07/14/03 - 10/13/03 07/14/03 - 10/13103 07/14/03 - 10/13103 07/14/03 - 10113/03 07/14/03 - 10113/03 07114/03 - 10/13/03 07114103 - 10/13/03 07114/03 - 10113103 07114/03 - 10113103 07/14/03 - 10/13/03 07/14103 - 10113103 07/14/03 - 10/13103 07/14/03 - 10/13103 07/14103 - 10/13/03 07/14/03 - 10113/03 07114/03 - 10113103 07114/03 - 10/13103 07/14103 - 10/13/03 07/14/03 - 10/13/03 07/14103 - 10113/03 07/14/03 - 10/13/03 07/14103 - 10/13/03 07/14103 - 10113/03 07/14103 - 10/13103 07/14103 - 10/13103 07/14/03 - 10/13103 07/14103 - 10/13103 07114/03 - 10/13103 07/14103 - 10/13/03 07/14103 - 10/13103 10/13/03 - 01/12/04 10113/03 - 01/12/04 10113103 - 01/12104 10/13/03 - 01/12104 10/13103 - 01/12104 10/13103 - 01/12/04 10/13103 - 01/12/04 10/13/03 - 01112/04 10/13/03 - 01112/04 10113/03 - 01/12/04 10113103 - 01/12/04 10113103 - 01/12/04 10113103 - 01/12/04 10/13103 - 01/12/04 10113103 - 01112/04 10113/03 - 01112/04 10/13/03 - 01112/04 10113/03 - 01/12/04 10113/03 - 01/12/04 10113/03 - 01112/04 10113103 - 01112/04 10113103 - 01112/04 10113103 - 01112104 10/13103 - 01112/04 10/13103 - 01112/04 10113103 - 01112/04 10/13/03 - 01112104 10113/03 - 01112/04 10/13/03 - 01)12104 10/13103 - 01112104 10/13/03 - 01112104 10/13/03 - 01112/04 10/13/03 - 01/12/04 10113103 - 01112/04 10/13/03 - 01112/04 10/13103 - 01112/04 10/13/03 - 01112/04 10113/03 - 01112/04 10113/03 - 01112/04 10/13103 - 01112/04 10113103 - 01112/04 10113/03 - 01112/04 10/13/03 - 01112/04 10/13/03 - 01112/04 C-23
Intentionally Left Blank
FIGURE C-1 MEAN COBALT-60 CONCENTRATION IN CLAMS OYSTER CREEK GENERATING STATION, 1983 - 2003 I........................................... INDICATOR STATION BACKGROUND STATION cJ 15.............................................................................................................................
c 10
.l
- d, l0 0
m in o
tl tl t"
00 00 Ci 0i 0F O
O V-P-
V-mm em em m
'I "T
ti tm cb m 00 X0 X
00 00 00 00 X0 X0 X0 X0 0fi
(
08 0E 08 0\\
0E 0fi 0\\
08 0fi Cf cF 0\\
0E 0i O
0%
0%
0%
0%
0%
0%0%
0%
0% 0 0
0%
c 0
0 0%
0%
0%
ok 0%0%
0%
t 0
m m %
0 YEAR
FIGURE C-2 MEAN COBALT-60 CONCENTRATION IN AQUATIC SEDIMENT OYSTER CREEK GENERATING STATION, 1984 - 2003 350 300
-9 INDICATOR STATION MEAN BACKGROUND STATION MEAN E
C; o
w 0
250 200 150 100 50 0
t inin o
t'-
t-t-
00 0%
0%
a-,
0
-in t-0%
-4 0 0 oo x
o0 0
0 0
0 o0 x
x 0 0 o0 0
o o
Os 0 0
0%
0%
0f %
0 0
0% 0%
0~
0%
0%
0%
01%
07%
0%
0%
0%
0%
ON ON as 0%
ON 0%
ON ON 0%
0%
0 0
0%
ON 0%
R%
00 YEAR
FIGURE C-3 MEAN CESIUM-137 CONCENTRATION IN AQUATIC SEDIMENT OYSTER CREEK GENERATING STATION, 1984 - 2003
-O INDICATOR BACKGROUND 600 I-I
-t 400.
I-0 U
200 t
It It tIn n
in In
%Z %Z %o t-t-
t x
0 00 %
f 0
e' m
It tn
'I 4 m
0 0 0 0 0 0 0 0 0 X
X 0
o0 X
0 0 0
oo 0
0 000 000 C0 0%
0 m
m 00 m%
0% 0 0
m o
C0%
0%
0% 0%0 C%
m 0%0 0%0 0% 0 0%0 C
0% 00 g
4 _
9-YEAR
FIGURE C-4 MEAN WEEKLY GROSS BETA CONCENTRATIONS IN AIR PARTICULATES OYSTER CREEK GENERATING STATION, 2003 o INDICATOR
- BACKGROUND 4.OOE-02 L
S.
ci
- = 3.OOE-O2 L
.2
(, 2.OOE-02 0
o 1.OOE-02 O.OOE+00 en
)
en en en e
0 0
0 0
0 I I I
I 0
0 0
(9M0
( 9 OQ
(
0 nX Date
FIGURE C-5 MEAN MONTHLY GROSS BETA CONCENTRATIONS IN AIR PARTICULATES OYSTER CREEK GENERATING STATION, 1984 - 2003 0.18 0.16
'N I CHERNOBYL ACCIDENT I..............T
-O-INDICATORSTATIONS BACKGROUND STATION
- 0.14 4.I.................................................................................................................
C)
C)
.00u CS C'
0.12-....
0.10 4...................................................................................................................
0.08-0.06 4.
0.04.............. I 0.02 0.00 i=..
TaWl~
B1S gss l W ~
f 1
1 111111 11 11 i 1§l 1l]{11 §sxWl§b{WXTI1 X~T §lI1 lllllllllm*--
It In
%0
%a 00 00 0%
0 0
i N
o
'1t Nl
%O t-0 x
0 %
0 0
N e 'M 00 0
0 00 0
00 00 00 00 0
0%
0%
0%
0%
ON 0
0%
0%
C.,
0 0% M 0
0 0
0 0
0 o0%
Q 0% o%
0%
0%
0%
C
% Q 0C M
M 0%
i M
0 0% Q
% 0% M e
0 0
0 0
0 0
0 I"
I
-4 V4
_ -t I
4 4
.4
.4 N
N N rl N
N
- Data from Cookstown station ONLY after December 1996 YEAR
FIGURE C-6 MEAN QUARTERLY TLD GAMMA DOSE OYSTER CREEK GENERATING STATION, 2003 20....... ill.
14 8.......a l:..
.... C.......................
C, Im-o
~I 12.
8..
O TO 2MILES 2 TO 5MILES OVER 5MILES DISTANCE RING FROM PLANT 0 Apr-03 Jul-03 ED Oct-03 0 Jan-041
FIGURE C-7 MEAN QUARTERLY TLD GAMMA DOSE OYSTER CREEK GENERATING STATION, 1989 - 2003
- 20 *---------- -.................................-----.........................................
O INDICATOR MEA
- BACKGROUND MNEA LIc 15.............................................................................................................................
U Po 5
= 10
-4 04.
0000 0%
0 0%
0%
0%
0%
0%
0%
0 Os 0%
0%
0%
0%
0%
m 0%
0%
0%
0r% 0 0
0 0
0 0
0 0
C 0%
O 0%
0%
0%
0%
0%
0%
0%
0%
0%
0%
0%
as h
0%
0%
all%0%
0%
0 0%
ON 0
0 00 0
0 0
C
~
_4 N
N N
N N
N Nx N
e ee Year Harshaw Model 110 TLDs were used during the first quarter of 2001. Panasonic Model 814 TLDs were used in the second, third, and fourth quarters of 2001.
I.
Intentionally Left Blank
APPENDIX D DATA TABLES QC LABORATORY
The following section contains data illustrating the analyses performed by the quality control laboratory, Teledyne Brown Engineering (TBE). Duplicate samples were obtained from several locations and media and split between the primary laboratory, Environmental Inc. (Env) and TBE. Comparison of the results for most media were within expected ranges.
D-1
Intentionally Lef Blank D-2
TABLE D-1.1 CONCENTRATIONS OF TRITIUM IN SURFACE WATER SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMA COLLECTION PERIOD 24 QCA QCB 04/14103 09/22103
< 190
< 184
< 179
< 193
< 1350
< 164 MEAN*
187 +/- 8 186 +/- 20 757 i 1677
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES D-3
TABLE D-1.2 STC COLLECTION PERIOD 24 04/14/03 09/22/03 MEAN*
OCA 04/14/03 09122103 MEAN*
QCB 04/14/03 09122103 MEAN*
CONCENTRATIONS OF GAMMA EMITTERS IN SURFACE WATER SAMPLES COLLECTED0 IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF PCIILITER +/- 2 SIGMA Mn-54 Co-58 Fe-59 Co-60 Zn-65 Zr-95 Nb-95 Cs-134 Cs-137
<2
<2
<6
<2
<4
<5
<3
<2
<2
<4
<4
<8
<4
<8
<7
<4
<3
<4 3.0 +/- 2.4 3.0 +/- 1.9 6.8 +/- 3.5 3.0 +/- 2.3 5.9 +/- 4.9 5.7 +/- 2.8 3.3 +/- 1.9 2.8 +/- 1.7 3.1 +/- 2.4
< 3
<3
<7
<3
<7
<6
<3
<3
<3
<4
<4
<8
<4
<7
<6
<4
<3
<4 3.3 +/- 0.9 3.4 +/- 0.4 7.5 +/- 0.5 3.2 +/- 1.0 7.0 +/- 1.1 6.0 +/- 0.2 3.6 i 0.2 2.9 +/- 0.6 3.4 +/- 0.7
< 1
< 1 4
<1
< 3
< 3
<2 1
< I
<4
<3
<12
<3
<5
<5
<4
<5
<5 2 +/-4 2 +/-2 8 +/- 12 2 +/-2 4 +/-2 4 +/-3 3 +/-4 3 +/-5 3 +/-5 Ba-140
< 23
< 17 20 +/- 8
< 31
< 17 24 +/- 19
<18
< 22 20 +/- 6 La-140
<8
< 6 7 +/-2
< 10
<6 7.9 +/- 5.1
<4
<4 4 +/- 1
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES
TABLE D-11.1 CONCENTRATIONS OF TRITIUM IN WELL WATER SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF PCI/LITER
- 2 SIGMA COLLECTION PERIOD 1
OCA QCB 12/11/02 - 02/14/03 03113103 - 05/07103 07102/03 - 09/16/03 09/06102 - 11107102
'c 191 c 176
' 189
' 186
' 192 c 176 c 189 c 188 136 c 152
< 164
' 160 MEAN*
186 i 13 186 +/- 14 153 t 25
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES D-5
TABLE D-11.2 CONCENTRATIONS OF GAMMA EMITTERS IN WELL WATER SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMA STC COLLECTION PERIOD Mn-54 Co-58 Fe-59 Co-60 Zn-65 Zr-95 Nb-95 Cs-134 Cs-137 Ba.140 La-140 1
12/11 03/13 07/02 11107 02/14/03
- 05/07/03
- 09/16/03
- 12/19/03
<3
<3
<6 (3
<5
<5
<3
<3
<3
<2
<3
<3
<5
<4
<3
<2
<5
<4
<8
<6
<9
<7
<4
<4
<2
<2
<6
<2
<4
<4
<2
<2 (3
<18
<3
<13
<4
<22
- 2
-49
< 6
<3 (7
< 15 MEAN*
3.1 +/- 2.6 2.8 +/- 1.3 5.8 +/- 3.8 3.2 +/- 3.4 5.8 +/- 4.0 5.1 +/- 2.6 2.9 +/- 1.5 2.5 +/- 1.6 2.8 +/- 2.1 25 +/- 32 7.5 +/- 9.9 QCA 1211 03/13 07/02 11107
- 02)14/03
- 05/07/03
- 09/16/03 12/19/03
<4
<4
<9
<4
<8
<7
<4
<3
<4
<24
<3
<3
<7
<3
<6
<6
<3
<3
<3
<16
<3
<3
<7
<3
<6
<6
<3
<3
<3
<16
< 2
<2
< 5
< 2
< 3
< 4
< 2
< I
< 1
< 41
<8 (5
(5
< 15 MEAN*
2.8 +/- 1.9 2.9 +/- 1.3 6.8 +/- 3.0 3.0 +/- 2.0 5.7 +/- 3.7 5.4 +/- 2.7 3.1 +/- 1.6 2.6 +/- 1.7 3.1 +/- 2.5 24 +/- 23 8.1
- 9.4 QCB 12)11 03127 07/02 09106
- 02/14/03
- 05/10/02
- 09/16/03
- 11/07/02 (3
<3
<11
<2
<3
<5
<4
<4
<11
<2
<2
<5
<3
<4
<10 (3
<6
<6
<6
<6
<8
<2
<4
<5
<4
<4
<5
<25
<2
<3
<2
<21
<5
<6
<7
<31
<4
<2
<2
<55
<6
<2 (7
( 9 MEAN' 2.8 +/- 1.7 2.8 +/- 1.2 8.3 +/- 6.8 3.3 +/- 3.2 4.8 +/- 2.0 7.3 +/- 4.5 3.8 +/- 2.0 3.7
- 2.9 3.9 +/- 4.6 33
- 30 6.2
- 5.7
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES
TABLE DI111.1 CONCENTRATIONS OF GAMMA EMITTERS IN CLAM SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF PCIIKG WET +/- 2 SIGMA STC COLLECTION K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 Cs-134 Cs-137 PERIOD 24 04115/03 1340 +/- 236
< 15
< 17
< 38
< 13
' 29
< 14
< 14 QCA 04/14/03 997 +/- 243
< 12
< 14
< 31
< 11
< 23
< 10
< 12 QCB 04/16/02 848 +/- 406
< 23
< 16
< 68
< 19
<46
< 25
< 14
TABLE D-IV.1 CONCENTRATIONS OF GAMMA EMITTERS IN SEDIMENT SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2002 STC COLLECTION PERIOD 24 04/14103 09/22V03 MEAN*
QCA 04/14103 09122V03 MEAN*
QCB 04114103 09122103 CD MEAN*
RESULTS IN UNITS OF PCI/KG DRY +/- 2 SIGMA Be-7 K-40 Mn-54 Co.58 Co-60 Cs-134 Cs-137 Ra-226 Th-232 j A
< 110
< 124 117 +/- 20
< 160
< 182 171
- 31
< 87
< 344 215 +/- 363
< 72 664
- 266 368 +/- 837 577
- 204 509 +/- 397 543
- 96 366
- 193 2081
- 398 1224 +/- 2424
< 9
< 15 12 +/- 8
< 14
< 19 16
- 6
< 11
< 19 15
- 13
<11
< 15 13
- 5
< 16
< 20 18 +/- 5
< 11
<21 16 +/- 13
< 10
<30 20 +/- 28
< 17
< 19 18 +/- 3
< 11 9
10 +/- 2
<9
<14 12
- 6
<13
<17 15
- 6
<10 4 17 13 +/- 10
< 11
< 17 14 +/- 8
< 14
<21 17
- 9
< 8
( 15 11 +/-9
< 191 601 +/- 376 284 +/- 262
< 314
< 413 364 +/- 140 613 +/- 365 4 395 421 +/- 328 142 +/- 83 191
- 42 62 +/- 58 119
- 42 181
- 107 74 +/- 92 NA NA 158 +/- 67
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES NA = NOT AVAILABLE
TABLE D-V.1 CONCENTRATIONS OF STRONTIUM AND GAMMA EMITTERS IN VEGETATION SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2003 RESULTS IN UNITS OF PCI/KG WET +/- 2 SIGMA STC COLLECTION Sr-89 PERIOD 36 CABBAGE AUGUST
< 12 TOMATOES AUGUST
< 10 TOMATOES SEPTEMBER
< 10 COLLARDS SEPTEMBER
< 8 Sr-90 K.40 1-131 Cs-134 Cs-137 Ba-140 La.140 3.8
- 1.9
'3
' 2 7.5
- 1.9 1950 i 190 2070
- 190 2200 i 206 3420 i 468
( 40
< 40
< 13
< 32
' 8 (9
9
< 18
' 10
<9
< 11 22
' 77
< 77
< 40
< 99
< 31
( 27
' 13
< 29 MEAN' 10 i3 29 5.3 2410
- 1362 31
- 26 11
- 10 13
- 12 74
- 49 25
- 18 OCA COLLARDS SEPTEMBER TOMATOES SEPTEMBER
< 16
( 10 22
- 3
( 2 4180
- 118 2290
- 93
' 12
' 11
<4
<4 (3
(3
< 28
' 24 MEAN*
13 9
12
- 28 3235
- 2673 12
- 2 3 +/- 1 4
- 1 26 i 5 8 *4 a
QCB CABBAGE CD COLLARDS AUGUST AUGUST
< 2 2406
- 305
< 3 3611 +/- 446
< 12 22
< 15
( 10
< 13
< 13
<50
< 60
< 8
< 18 MEAN*
5
- 3 2 +/- 1 3008
- 1704 17
- 14 13
- 8 13
- 0 55 4 15 13 +/- 14
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES
APPENDIX E INTER-LABORATORY COMPARISON PROGRAM
TABLE E-1 ANALYTICS ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING, 2003 (PAGE I OF 3)
Identification Reported Known Ratio (c)
Month/Year Number Matrix Nuclide Units Value (a) Value (b) TBE/Analytics Evaluation (d)
March, 2003 E3585-396 Milk Sr-89 Sr-90 pCi/L 80 133 pCUL 11.2 11.8 0.60 0.95 N(1)
A E3586-396 Milk E3588-396 AP 1-131 Ce-141 Cr-51 Cs-134 Cs-137 Co-58 Mn-54 Fe-59 Zn-65 Co-60 Ce-141 Cr-51 Cs-134 Cs-137 Co-58 Mn-54 Fe-59 Zn-65 Co-60 pCiU pCilL pCi/L pCi/
pCii/L pCi/L pCi/L pCiJL pCitL pCilL pCi pC pci pCi pCi pci pC pC pCi 75 168 243 83 207 49 65 53 114 169 239 348 101 277 66 97 80 152 223 74 173 246 90 200 47 64 47 93 162 224 318 117 259 60 83 61 120 209 1.01 0.97 0.99 0.92 1.04 1.04 1.02 1.13 1.23 1.04 1.07 1.09 0.86 1.07 1.10 1.17 1.31 1.27 1.07 A
A A
A A
A A
A W
A A
A A
A A
A N (2)
W A
E3587-396 Charcoal 1-131 pci 68 74 0.92 1.05 0.87 A
A A
June.2003 E3747-396 Milk Sr-89 Sr-90 pCi.L 89 85 pCiUL 20 23 E3748-396 Milk E3750-396 AP 1-131 Ce-141 Cr-51 Cs-134 Cs-137 Co-58 Mn-54 Fe-59 Zn-65 Co-60 Ce-141 Cr-51 Cs-134 Cs-137 Co-58 Mn-54 Fe-59 Zn-65 Co-60 pCilL pCi/L pCilL pCi/L pCilL pCUL pCilL pCiUL pCilL pCilL pCi pCi pCi pCi pCi pCi pCi pCi pCi 115 285 266 99 236 106 190 108 208 142 238 239 79 189 71 164 91 155 109 103 283 239 103 230 93 186 99 181 132 248 209 91 202 81 163 87 159 116 1.12 1.01 1.11 0.96 1.03 1.14 1.02 1.09 1.15 1.08 0.96 1.14 0.87 0.94 0.88 1.01 1.05 0.97 0.94 A
A A
A A
A A
A A
A A
A A
A A
A A
A A
E-1
TABLE E-1 ANALYTICS ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING, 2003 (PAGE 2 OF 3)
Identification Reported Known Ratio (c)
MonthlYear Number Matrix Nuclide Units Value (a) Value (b) TBE/Analytics Evaluation (d)
June,2003 E3749-396 Charcoal 1-131 pci 78 62 September, 2003 E3898-396 Milk E3899-396 Milk Sr-89 Sr-90 1-131 Ce-141 Cr-51 Cs-134 Cs-137 Co-58 Mn-54 Fe-59 Zn-65 Co-60 pCVL 45 100 pCi/L 13 14 E3901-396 AP Ce-141 Cr-51 Cs-134 Cs-1 37 Co-58 Mn-54 Fe-59 Zn-65 Co-60 E3900-396 Charcoal 1-131 pCi/L pCirL pCi/L pC/L pCi/L pCVL pCi/L pCilL pCi/L pCilL pci pci pC!
pci pci pci pci pci pci pci 73 85 220 106 90 96 95 84 187 132 79 227 93 70 80 73 74 143 93 74 86 233 119 88 99 93 79 176 123 77 210 108 79 89 84 71 158 111 1.26 0.45 0.93 0.99 0.99 0.94 0.89 1.02 0.97 1.02 1.06 1.06 1.07 1.03 1.08 0.86 0.89 0.90 0.87 1.04 0.91 0.84 0.86 W
N Ci)
A A
A A
A A
A A
A A
A A
A A
A A
A A
A A
A 74 86 November, 2003 E3790-396 Milk E3971-396 Milk Sr-89 Sr-90 1-131 Ce-141 Cr-51 Cs-134 Cs-137 Co-58 Mn-54 Fe-59 Zn-65 Co-60 pCi/L pCi/L pCiVL pCi/L pCi/L pCi/L pCilL pCiIL pCi/L pCi/L pCi/L pCi/L 185 19 87 186 287 119 116 111 176 94 190 140 168 17 90 202 280 135 129 111 173 102 197 155 1.10 1.12 A
A 0.97 0.92 1.03 0.88 0.90 1.00 1.02 0.92 0.96 0.90 A
A A
A A
A A
A A
A E-2
TABLE E-1 ANALYTICS ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING, 2003 (PAGE 3 OF 3)
Identification Reported Known Ratio (c)
Month/Year Number Matrix Nuclide Units Value (a) Value (b) TBE/Analytics Evaluation (d)
November. 2003 E3973-396 AP Ce-141 Cr-51 Cs-134 Cs-137 Co-58 Mn-54 Fe-59 Zn-65 Co-60 pCi pCi pCi pCi pCi PC!
pCi pCi PC!
144 203 90 85 80 115 72 121 102 142 198 96 91 78 122 72 139 109 1.01 1.03 0.94 0.93 1.03 0.94 1.00 0.87 0.94 A
A A
A A
A A
A A
E3972-396 Charcoal 1-131 pCi 67 77 0.87 A
(1) Incorrectly calculated. The recalculated March & September Sr-89 results of 138 & 95.8pCi/
respectively, are acceptable.
The efficiency required for these samples is different than the eftciencyforregularsamples NCR 04-02 (2) Using only the results from the 1099.2 keVphoton. the Fe-59 would be 71 pCi. Wich Ls acceptable. Coincidental summing occurs only with significant Fe-59 activity levels. Therefore, there Is no impact on environmental samples NCR 04-02 (a) Teledyne Brown Engineering reported result.
(b) The Analytics known value Is equal to 1000% of the parameterpresent in the standard as determined bygravimetric and/or volumetric measurements made during standard preparation.
(c) Ratb of Teledyne Brown Engineering to Analytics results (d) Analytics evaluation based on TBEintemal QClimits:A=Acceptable. Reportedresultfalls within ratio imits of.80-1.20.
W-Acceptable with waming. Reportedresult falls within.70-0.80 or 1.20-1.30. N= NotAcceptable. Reported result falls outside the ratio limits of < 0.70 and > 1.30.
E-3
TABLE E-2 DOEIEML ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING, 2003 (PAGE 1 OF2)
Identification Reported Known Ratio (c)
Month/Year Number Media Nuclide Units Value (a) Value (b)
TBE/EML Evaluation (d)
March, 2003 QAP 58 AP (QAP 0303)
Soil Co-60 Cs-137 Gr-Beta Mn-54 Sr-9O A-228 Bi-212 Bi-214 Cs-137 K-40 Pb-212 Pb-214 Sr-90 Th-234 Bqffilter 35.9 33.5 Bqffilter 113.7 99.7 Bq/filter 1.6 1.5 Bqlfilter 49.4 43.8 Bqlfilter 2.4 2.8 Bqlkg 70.2 57.06 Bqlkg 72.5 60.6 Bqlkg 76.2 67.0 Bq/kg 1883 1450 Bqtkg 805.7 636 Bq/kg 74.8 57.9 Bqtkg 79.2 71.1 Bq/kg 53.5 64.4 Bqtkg 169.1 127 Bqlkg 14.4 12.1 Bqlkg 522 444 Bqlkg 1360 1120 Bqlkg 498.3 650 1.07 1.14 1.07 1.13 0.86 1.23 1.20
.1.14 1.30 1.27 1.29 1.11 0.83 1.33 1.19 1.18 1.21 0.77 A
A A
A A
W W
A N (i)
W W
A A
A A
A A
A Vegetation CoG0 Cs-137 K40 Sr-90 Water Co-60 Cs-134 Cs-137 Gr-Beta H-3 Sr-9o September, 2003 QAP 59 AP (QAP 0309)
Soil Mn-54 Co-60 Sr-90 Cs-137 Gr-Beta K-40 Sr-90 Cs-137 Bi-212 Pb-212 Bi-214 Pb-214 Ac-228 Th-234 Bq/L 252.3 234 Bq/L 31.1 30.5 Bq/L 71.5 63.8 Bq/L 821.3 627.5 Bq/L 418.3 390 Bq/L 3.63 4.34 Bqlfilter 54.0 58.0 Bqtfilter 53.3 55.1 Bq/filter 1.7 2.058 Bqtfilter 51.2 54.8 Bq/filter 3.4 3.89 Bq/kg 517.0 488.0 Bq/kg 70.0 80.3 Bqlkg 2127.0 1973.0 Bqlkg 56.1 53.9 Bqlkg 52.7 50.7 Bqlkg 36.4 34.4 Bqlkg 41.5 35.2 Bqlkg 56.2 50.8 Bqlkg 145.4 116.0 1.08 1.02 1.12 1.31 1.07 0.84 0.93 0.97 0.83 0.93 0.87 1.06 0.87 1.08 1.04 1.04 1.06 1.18 1.11 1.25 A
A W
W A
W A
A A
A W
A A
A A
A A
A A
A E-4
TABLE E-2 DOEIEML ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING, 2003 (PAGE 2 OF 2)
Identification Reported Known Ratio (c)
Month/Year Number Media Nuclide Units Value (a) Value (b)
TBE/EML Evaluation (d)
September, 2003 QAP 59 (QAP 0309)
Water H-3 Co-60 Sr-90 Cs-134 Cs-137 Gr-Beta Bq/L BqIL Bq/L Bq/L Bq/L Bq/L 511.0 491.0 5.9 62.4 74.9 1663.0 446.3 513.0 7.04 63.0 80.3 1948.0 1.14 0.96 0.84 0.99 0.93 0.85 A
A W
A A
A (1) Incorrect bottle size used. Sample was placed into a smaller containerand recounted. Al recount results were acceptable except i-212 which was acceptable with arming Previouslyanalyzed samples were examinedandno otherincorrectcontainersizes were noted. NCR 03-07 (a) Teledyne Brown Engineering reported result (b) The DOEiEML known value is equal to 100%Y of the parameterpresent in the standard as determined by gravimetric and/or volumetric measurements made during standard preparation (c) Ratio of Teledyne Brown Engineering to DOEIEML results.
(d) DOE/EML evaluation: A=acceptable. W=acceptable with warning. N=not acceptable.
E-5
TABLE E-3 ERA ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING, 2003 (PAGE 1 OF 1)
Identification Reported Known Month/Year Number Media Nuclide Units Value (a) Value (b) Control limits Evaluation (c)
May, 2003 Rad 53 Water 1-131 H-3 Co-60 Cs-134 Cs-137 Sr-89 Sr-90 pCi/L pCi/L pCiIL pCi/L pCiVL pCi/L pCiIL 13.6 1200 69.9 73.5 165 37.0 23.5 20.8 1250 63.8 75.7 150 31.3 27.4 15.6 - 26.0 678 - 1820 55.1 - 72.5 67.0 -84.4 141 - 159 22.6 -40.0 18.7 -36.1 N(1)
A A
A N (2)
A A
November, 2003 Rad 55 Water 1-131 H-3 Co-60 Cs-134 Cs-137 Sr-89 Sr-90 Gr-Beta pCVIL pCi/L pCVL pCVL pCiIL pCilL pCiIL pC!IL 22.2 1630 28.4 21.7 63.6 47.9 9.23 161 28.2 14300 27.7 23.4 64.2 50.4 10.2 168 23.0 - 33.4 11800 -16800 19.0 -36.4 14.7 - 32.1 55.5 - 72.9 41.7-59.1 1.54-18.9 124 - 212 N (3)
N (3)
A A
A A
A A
(1) The stable iodine caerir n the sample was unaccounted for In the calculation. When recalculated, the conect result of 20.0pCVZL was within acceptance critenfa. NCR 03-11 (2) Although Cs-137is evaluatedas N. the TBE/ERA ratio of 1.10 falls within limits of 0.80 - 1.20 and Is considered by TBEas acceptable.
(3) The decay conetion did not take into account the extended count time. When recalculated, the conect result of 23.2 was within acceptance criteria. NCR 04-06 Due to recalculating H-3 to required reporting units. a decimalplace was dropped. The correct result of 16300 is within acceptance criteria. NCR 04-06 (a) Teledyne Brown Engineeing reported result.
(b) The ERA known value is equal to 1OO of the parameterpresent In the standard as determined by gravimetric and/or volumetric measurements made during standardpreparation.
(c) ERA evaluation: A=acceptable. Reported result falls within the Waming Limits. NA=not acceptable. Reported result falls outside of the Control Limits. CE=check for Ermr. Reported result falls within the Control Limits and outside of the Waming Limit E-6
TABLE E-4 MAPEP ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING, 2003 (PAGE 1 OF 1)
Identification Reported Known Month/Year Number Media Nuclide Units Value (a) Value (b)
Control Limits Evaluation (c)
February, 2003 02-W10 Water Cs-1 34 Bq/L 382.7 421 294.70 - 547.30 Cs-1 37 Bq/L 329.3 329 230.30 - 427.70 Co-57 Bq/L 58.17 57 39.90 - 74.10 Co-60 Bq/L 41.2 38.2 26.74 - 49.66 Mn-54 Bq/L 35.07 32.9 23.03 - 42.77 Sr-90 Bq/L 11.70 12.31 8.62-16.00 Zn-65 Bq/L 566 516 361.20 - 670.80 Cs-1 34 Bq/Kg 204 238 166.60 - 309.40 Cs-137 Bq/Kg 803 832 582.40- 1081.60 Co-57 Bq/Kg 499 530 371.00 -689.00 Co-60 Bq/Kg 427 420 294.00 - 546.00 Mn-54 Bq/Kg 136 137 95.90- 178.10 K-40 Bq/Kg 686 652 456.40 - 847.60 Sr-90 Bq/Kg 651 714 499.80 - 928.20 Zn-65 Bq/Kg 528 490 343.00 - 637.00 A
A A
A A
A A
A A
A A
A A
A A
July, 2003 03-SlO Soil (a) Teledyne Brown Engineering reported result.
(b) The MAPEP known value is equal to 100%Y of the parameterpresent in the standard as deternined by gravimetric and/or volumetric measurements made during standard preparation.:
(c) DOE/MAPEP evaluation: A=acceptable, WHacceptable with warning, N=not acceptable.
E-7
TABLE E-5 ERA(8) STATISTICAL
SUMMARY
PROFICIENCY TESTING PROGRAM ENVIRONMENTAL, INC., 2003 (Page I of 2)
Concentration (pCUL)
Lab Code Date Analysis Laboratory ERA Control Resuleb Resultc Limits STW-973 02/17/03 STW-973 02/17/03 STW-974 02117/03 S1W-974 02/17/03 STW-974 02/17/03 STW-974 02/17/03 STW-974 02/17/03 STW-975' 02/17/03 STW-975 02/17/03 STW-976 02/17/03 STW-976 02/17/03 STW-976 02117/03 Sr-89 Sr-90 Ba-133 Co-60 Cs-134 Cs-137 Zn-65 Gr. Alpha Gr. Beta Ra-226 Ra-228 Uranium 17.0 0.5 8.9 *0.3 14.5
- 09 37.5
- 0.9 18.2 *0.6 42.7 +/-1.0 56.8 *2.2 18.4 +/-0.3 11.7 +/-0.5 4.1 +/-0.1 7.6 +/-0.5 52.9 +/-1.9 15.9
- 5.0 9.0 +/- 5.0 19.5 +/- 5.0 37.4 +/- 5.0 17.8 +/- 5.0 44.2 +/- 5.0 60.3 +/- 6.0 37.6 +/- 9.4 8.6 +/- 5.0 4.7 +/- 0.7 6.5 +/- 1.6 53.7 +/- 5.4 7.2 -24.6 0.4 -17.7 10.8 -28.2 28.7 -46.1 9.1 -26.5 35.5 - 52.9 49.9 -70.7 21.3 - 53.9 0.0 -17.2 3.5 -6.0 3.7 - 9.3 44.4 - 63.0 STW-983 05/19/03 S1W-984 05/19/03 S1W-985 05/19/03 STW-985 05/19/03 STW-985 05/19/03 STW-985 05119/03 S1W-986 05119/03 S1W-986 05/19/03 S1W-986 05/19/03 STW-986 05/19/03 S1W-986 05/19/03 STW-986 05/19/03 H-3 1-131 Gr. Alpha Ra-226 Ra-228 Uranium Co-60 Cs-134 Cs-137 Gr. Beta Sr-89 Sr-90 1290.0 +/-25.0 19.7 +/-1.3 54.4 +/- 3.0 14.9 +/-0.2 13.1 +/-0.6 14.5 +/-0.4 56.9 +/- 8.6 61.6 +/-6.6 143.0 +/-1.2 309.0 +/-2.7 33.1 +/-0.2 28.8 +/- 1.3 1250.0 +/- 331.0 20.8 +/- 3.0 70.3 +/- 17.6 16.5 +/- 2.5 10.3 +/- 2.6 15.1 +/-3.0 63.8 +/- 5.0 75.7 +/- 5.0 150.0 +/- 7.5 363.0 +/- 54.5 31.3 +/- 5.0 27.4 +/- 5.0 678.0 - 1820.0 15.6 -26.0 39.9 -101.0 12.2 -20.8 5.8 - 14.8 9.9 -20.3 55.1 -72.5 67.0 -84.4 137.0 -163.0 269.0 -457.0 22.6 -40.0 18.7 -36.1 STW-988 08/18/03 STW-988 08/18/03 STW-988 08118103 S1W-989 08118/03 STW-989 08/18/03 S1W-989 08/18103 S1W-989 08/18/03 STW-989 08/18/03 STW-990 08/18/03 STW-990' 08/18103 STW-991 08/18103 STW-991 08/18/03 Ra-226 Ra-228 Uranium Ba-133 Co-60 Cs-134 Cs-137 Zn-65 Gr. Alpha Gr. Beta Sr-89 Sr-90 13.3 +/-1.1 11.5 +/- 1.0 12.3 +/-0.4 18.1 +/-1.9 35.9 +/- 1.3 32.6 +/- 1.8 48.3 +/- 0.6 58.9 +/- 2.1 41.8 +/-3.4 51.3 +/-3.0 57.2 +/- 4.3 21.2 +/-0.9 13.4 +/-2.0 12.5 +/- 3.1 11.4 +/-3.0 20.7 +/- 5.0 37.4 +/- 5.0 32.6 +/- 5.0 44.3 +/- 5.0 60.2 +/- 6.0 56.2 +/- 16.3 31.6 +/- 5.0 58.8 +/- 5.0 20.6 +/- 5.0 9.9 -16.9 7.1 -17.9 6.2 -16.6 12.0 -29.4 28.7 -46.1 23.9 -41.3 35.6 - 53.0 49.8 -70.6 36.9 - 93.3 22.9 -40.3 50.1 -67.5 11.9 -29.3 E-8
TABLE E-5 ERA(") STATISTICAL
SUMMARY
PROFICIENCY TESTING PROGRAM ENVIRONMENTAL, INC., 2003 (Page 2 of 2)
Concentration (pCVL)
Lab Code Date Analysis Laboratory ERA Control Resultb Resultc Limits STW-997 STW-997 S1W-998 STW-999 STW-999 STW-999 STW-1000 STW-1001 STW-1001 S1W-1001 STW-1001 STW-1002 STW-1002 S1W-1002 S1W-1002 S1W-1002 STW-1002 11/18/03 11/18103 11/18/03 11/18/03 11118/03 11/18/03 11118/03 11/18/03 11/18/03 11/18/03 11/18/03 11/18/03 11/18/03 11/18/03 11/18/03 11/18/03 11/18/03 Gr. Alpha Gr. Beta 1-131 Ra-226 Ra-228 Uranium H-3 Gr. Alpha Ra-226 Ra-228 Uranium Co-60 Cs-134 Cs-137 Gr. Beta Sr-89 Sr-90 37.0 +/- 2.0 26.5 +/-I 0.8 14.8 +/- 0.3 17.2 +/-1.1 6.6 +/- 0.3 11.7 +/- 0.3 15900.0 +/- 174.0 32.9 +/- 0.3 16.5 +/- 0.9 6.2 +/- 0.5 9.7 +/- 1.5 27.7 +/- 1.9 21.5 +/- 1.1 66.3 +/- 2.8 159.0 +/- 2.5 48.5 +/- 0.4 10.1 +/-3.0 29.5 +/-7.4 26.3 +/- 5.0 16.5 +/- 3.0 17.8 +/- 2.7 6.8 +/- 1.7 11.7 +/- 3.0 14300.0 +/- 1430.0 54.2 +/- 3.0 16.1 +/-2.4 5.5 +/- 1.4 9.3 +/- 13.6 27.7 +/- 5.0 23.4 +/- 5.0 64.2 +/- 5.0 168.0 +/- 5.0 50.4 +/- 5.0 10.2 +/- 25.2 16.7 -42.3 17.6 - 35.0 11.3 - 21.7 13.2 -22.4 3.8 - 9.7
.6.5 -16.9 11800.0 -16800.0 30.7 - 77.7 11.9 - 20.3 3.1 - 7.9 4.1 -14.5 19.0 - 36.4 17.6 -29.2 55.5 - 72.9 124.0 -212.0 41.7 - 59.1 1.5 -18.9 Results obtained by Environmental, Inc.. Midwest Laboratory as a participant In the environmental samples crosscheck program operated by Environmental Resources Associates (ERA).
b Unless otherwise indicated, the laboratory result is given as the mean +/- standard deviation for three determinations.
c Results are presented as the known values, expected laboratory precision (1 sigma, I determination) and control limits as provided by ERA.
d Recount of the original sample still low. The ERA blank was spiked In the lab; known value of 20.1 pCilL, measured 21.5* 1.1 pCilL No explanation for ERA test failure.
Lower bias observed for gamma spectroscopic analysis. The undiluted sample was reanalyzed; Results of reanalysis. Co-60: 62.3 pCiJL, Cs-134: 69.2 pCi/L., Cs-137: 152.3 pCi/L Reason for deviation unknown. A recount of the original planchets averaged 43.4 pCi/L.
Cs-1 37activity by gamma spectroscopy; 28.3 pCilL. Result of reanalysis; 29.3 pCi/L.
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TABLE E-6 DOE's Mixed Analyte Performance Evaluation Program (MAPEP)P.
Environmental, Inc., 2003 (Page 1 of 1)
Concentrationb Known Control Lab Code Type Date Analysis Laboratory result Activity Limitsc STW-972 STW-972 STW-972 STW-972 STW-972 STW-972 STW-972 STW-972 STW-972 STW-972 STW-972 STW-972 STW-972 STW-972 STW-972 STSO-987 STSO-987 STSO-987 STSO-987 STSO-987 STSO-987 STSO-987 STSO-987 STSO-987 STSO-987 STSO-987 STSO-987 STSO-987 water water water water water water water water water water water water water water water soil soil soil soil soil soil soil soil soil soil soil soil soil 12101/02 12/01102 12/01/02 12101/02 12V01102 12/01/02 12/01/02 12/01/02 12/01/02 12101/02 12/01/02 12/01/02 12/01/02 12101/02 12101/02 01/01103 01/01/03 01/01/03 01/01/03 01/01/03 01/01/03 01/01/03 01/01/03 01/01/03 01/01/03 01/01/03 01/01/03 01/01/03 Am-241 Co-57 Co-60 Cs-134 Cs-137 Fe-55 Mn-54 Ni-63 Pu-238 Pu-239/40 Sr-90 Tc-99 U-233/4 U-238 Zn-65 Co-57 Co-60 Cs-134 Cs-137 K-40 Mn-54 Ni-63 Pu-238 Pu-239/40 Sr-90 U-23314 U-238 Zn-65 0.56 :t0.06 57.10 +/-1.90 38.30
- 0.60 395.30 +/-10.10 316.40 +/-5.30 94.90 +/-24.50 33.40 +/-0.10 123.80
- 5.50 0.66 +/- 0.06 0.001 +/- 0.001 13.80 +/- 1.00 128.10 +/-3.80 1.60 +/- 0.09 1.64 +/- 0.09 540.40 +/- 9.90 534.36 +/- 2.61 442.16 +/-2.31 211.00 +/-2.30 849.50 +/- 3.30 716.50 +/-:12.80 148.76 +/-2.84 597.10 +/-23.50 67.05
- 3.10 52.80 +/- 3.60 609.50 : 9.80 99.50 +/-7.60 508.60 +/- 42.20 492.70 +/-28.10 0.58 +/- 0.09 57.00 +/- 5.70 38.20 +/- 3.82 421.00 +/-42.10 329.00 +/- 32.90 96.00 +/- 9.60 32.90 +/- 3.29 136.50 +/- 13.70 0.83 +/- 0.08 0.000 +/- 0.000 12.31 +/- 1.23 132.00 +/- 13.20 1.54 +/-0.15 1.60 +/- 0.16 516.00 +/- 51.60 530.00 +/- 53.00 420.00 +/- 42.00 238.00 +/- 23.80 832.00 +/- 83.20 652.00 +/- 65.20 137.00 +/- 13.70 770.00 +/- 77.00 66.90 +/- 6.70 52.70 +/- 5.30 714.00 +/- 71.40 89.00 +/- 8.90 421.00 +/-42.10 490.00 +/- 49.00 0.40 - 0.75 39.90 - 74.10 26.74 -49.66 294.70 - 547.30 230.30 - 427.70 67.20 - 124.80 23.03 -42.77 95.55 - 177.45 0.58 - 1.08 0.000 - 0.005 8.62 - 16.00 92.40 - 171.60 1.08 -2.00 1.12 -2.08 361.20 -670.80 371.00 - 689.00 294.00 - 546.00 166.60 -309.40 582.40 - 1081.60 456.40 -847.60 95.90 - 178.10 539.00 -1001.00 46.83 - 86.97 36.90 - 68.50 499.80 - 928.20 62.30 -115.70 294.70 - 547.30 343.00 -637.00 a Results obtained by Environmental, Inc.,Midwest Laboratory as a participant in the Department of Energy's Mixed Analyte Performance Evaluation Program, Idaho Operations office, Idaho Falls, Idaho b All results are in Bq/kg or Bq/L as requested by the Department of Energy.
C MAPEP results are presented as the known values and expected laboratory precision (1 sigma, 1 determination) and control limits as defined by the MAPEP.
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