ML031280240
| ML031280240 | |
| Person / Time | |
|---|---|
| Site: | Oyster Creek |
| Issue date: | 04/30/2003 |
| From: | Harkness E AmerGen Energy Co, British Energy Co, Exelon Corp |
| To: | Document Control Desk, Office of Nuclear Reactor Regulation |
| References | |
| 2130-03-20122 | |
| Download: ML031280240 (98) | |
Text
Amer Gen SM AmerGen Energy Company, LLC An Exelon/BTAtish Energy Company Oyster Creek US Route 9 South PO Box 388 Forked River, NJ 08731-0388 Technical Specification 6.9.1.e April 30, 2003 2130-03-20122 U. S. Nuclear Regulatory Commission Attention: Document Control Desk Washington, DC 20555
Subject:
Oyster Creek Generating Station Docket No. 50-219 1
Radiological Environmental Operating Report - 2002 Enclosed is a copy of the Oyster Creek Radiological Environmental Operating Report for the calendar year 2002. This submittal is made in accordance with Oyster Creek Generating Station Technical Specification 6.9.1.e.
If you should have any questions or require any further information, please contact Mr. John Rogers, of my staff, at 609-971-4893.
Very truly yours, Ernest J. Harkness P.E., Vice President Oyster Creek Generating Station EJH/JJR Enclosure cc:
Administrator, Region I NRC Project Manager NRC Sr. Resident Inspector
V -
-E i Docket No:
50-219 OYSTER CREEK GENERATING STATION UNIT 1 Annual Radiological Environmental Operating Report 1 January Through 31 December 2002 Prepared By Teledyne Brown Engineering Environmental Services 9M An Exelon/British nergy Company Oyster Creek Generating Station Forked River, NJ 08731 May 2003
1
41 Table Of Contents I. Summary and Conclusions................................
1 Il. Introduction........................................................................................................................2 A. Objectives of the REMP...............................
2 B. Implementation of the Objectives................................
3 Ill. 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...........................
8 A. Aquatic Environment...........................
8
- 1. Surface W ater............................................................ 8
- 2. Well Water........................
8
- 3. Fish...........................
9
- 4. Clams and Crabs.........................
9
- 5. Sediment................................................................................................... 10 B. Atmospheric Environment..........................
10
- 1. Airborne....................................................................................................10
- a. Air Particulates............................
10
- b. Airbome Iodine............................
11
- 2. Terrestrial 12
- a. Vegetation............................
12 C. Ambient Gamma Radiation.........................
12 D. Land Use Survey.............................
13 V. References............................
14 i
Appendices Appendix A Radiological Environmental Monitoring Report Summary Tables Table A-1 Radiological Environmental Monitoring Program Annual Summary for the Oyster Creek Generating Station, 2002 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, 2002 Radiological Environmental Monitoring Program - Summary of Sample Collection and Analytical Methods, Oyster Creek Generating Station, 2002 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 Concentrations of Tritium in Surface Water Samples Collected in the Vicinity of Oyster Creek Generating Statiorn, 2002.
Concentrations of Gamma Emitters in Surface Water Samples Collected in the Vicinity of Oyster Creek Generating Station, 2002.
Concentrations of Tritium in Well Water Samples Collected in the Vicinity of Oyster Creek Generating Station, 2002.
Concentrations of Gamma Emitters in Well Water Samples Collected in the Vicinity of Oyster Creek Generating Station, 2002.
Table C-11.1 Table C-11.2 ii
I.
Table C-111.1 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-Vll.1 Table C-V111.1 Table C-VNIl.2 Table C-VlII.3 Table C-IX.1 Figures Figure C-1 Figure C-2 Figure C-3 Figure C-4 Concentrations of Gamma Emitters in Predator and Bottom Feeder (Fish) Samples Collected in the Vicinity of Oyster Creek Generating Station, 2002.
Concentrations of Gamma Emitters in Clam and Crab Samples Collected in the Vicinity of Oyster Creek Generating Station, 2002.
Concentrations of Gamma Emitters in Sediment Samples Collected in the Vicinity of Oyster Creek Generating Station, 2002.
Concentrations of Gross Beta in Air Particulate Samples Collected in the Vicinity of Oyster Creek Generating Station, 2002.
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, 2002.
Concentrations of Strontium in Air Particulate Samples Collected in the Vicinity of Oyster Creek Generating Station, 2002.
Concentrations of Gamma Emitters in Air Particulate Samples Collected in the Vicinity of Oyster Creek Generating Station, 2002.
Concentrations of 1-131 in Air Iodine Samples Collected in the Vicinity of Oyster Creek Generating Station, 2002.
Concentrations of Strontium and Gamma Emitters in Vegetation Samples Collected in the Vicinity of Oyster Creek Generating Station, 2002.
Quarterly TLD Results for Oyster Creek Generating Station, 2002.
Mean Quarterly TLD Results for the Site Boundary, Middle, Special Interest, and Control Locations for Oyster Creek Generating Station, 2002.
Summary of the Ambient Dosimetry Program for Oyster Creek Generating Station, 2002.
Summary of Collection Dates for Samples Collected in the Vicinity of Oyster Creek Generating Station, 2002.
Mean Cobalt-60 Concentration in Clams Oyster Creek Generating Station, 1983 - 2002.
Mean Cobalt-60 Concentration in Aquatic Sediment Oyster Creek Generating Station, 1984 - 2002.
Mean Cesium-137 Concentration in Aquatic Sediment Oyster Creek Generating Station, 1984 - 2002.
Mean Weekly Gross Beta Concentrations in Air Particulates Oyster Creek Generating Station, 2002.
iii
Figure C-5 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 Monthly Gross Beta Concentrations in Air Particulates Oyster Creek Generating Station, 1984 - 2002.
Mean Quarterly TLD Gamma Dose Oyster Creek Generating Station, 2002.
Mean Quarterly TLD Gamma Dose Oyster Creek Generating Station, 1989 - 2002.
Data Tables and Figures - QC Laboratory Concentrations of Tritium in Surface Water Samples Collected in the Vicinity Of Oyster Creek Generating Station, 2002.
Concentrations of Gamma Emitters in Surface Water Samples Collected in the Vicinity of Oyster Creek Generating Station, 2002.
Concentrations of Tritium in Well Water Samples Collected in the Vicinity of Oyster Creek Generating Station, 2002.
Concentrations of Gamma Emitters in Well Water Samples Collected in the Vicinity of Oyster Creek Generating Station, 2002.
Concentrations of Gamma Emitters in Clam Samples Collected in the Vicinity of Oyster Creek Generating Station, 2002.
Concentrations of Gamma Emitters in Sediment Samples Collected in the Vicinity of Oyster Creek Generating Station, 2002.
Concentrations of Gamma Emitters in Vegetation Samples Collected in the Vicinity of Oyster Creek Generating Station, 2002.
Inter-Laboratory Comparison Program Analytics Environmental Radioactivity Cross Check Program Teledyne Brown Engineering Environmental Services DOE/EML Environmental Radioactivity Cross Check Program Teledyne Brown Engineering Environmental Services ERA Environmental Radioactivity Cross Check Program Teledyne Brown Engineering Environmental Services MAPEP Environmental Radioactivity Cross Check Program Teledyne Brown Engineering Environmental Services ERA Statistical Summary Proficiency Testing Program Environmental, Inc., 2002 DOE's Mixed Analyte Performance Evaluation Program (MAPEP)
Environmental, Inc., 2002 iv
11 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 2002 through 31 December 2002. During that time period, 938 analyses were performed on 810 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 in two surface water indicator stations and at the control station.
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 levels consistent with those detected in previous years. All strontium-89 results were below the minimum detectable activity. Strontium-90 activity was detected in all stations.
Environmental gamma radiation measurements were performed quarterly using thermoluminescent dosimeters. Levels detected were consistent with those observed in previous years.
I
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 1/4 mile west of the highway and 1/ miles east of the Parkway. The site property extends about 21/2 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, and Environmental Inc. (Midwest Labs) on samples collected during the period 01 January 2002 through 31 December2002.
A.
Objective 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.
- 6.
Evaluate the relationship between quantities of radioactive material 2
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 2002. 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 Environment 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 (control)). One annual crab sample was collected from one location (93).
3
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). Location 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 814 calcium sulfate (CaSO4) thermoluminescent dosimeters (TLD). The TLD locations were placed on and around the OCGS site as follows:
A site boundairy 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 rins consisting of 16 locations (6, 8, 22, 68, 73, 74, 75, 78, 79, 81, 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 locatioms consisting of 10 locations (3, 9, 11, 71, 72, 88, 89, 90, 92, and T1) representing special interest areas such as population centers, state parks, etc.
The balance of two locations (C and 14) representing control locations.
Indicator TLDs were placed systematically, with at least one station in each of 16 meteorological compass sectors (in a ring), typically within 0.25 miles of the OCGS, or as close as reasonable highway access would 4
permit. TLDs were also placed in each of the 16 sectors within a five mile radius of the OCGS, 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 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 2002. 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 The radiological and direct radiation data collected from past years was used for comparison and trending with 2002 operational data. For the purpose of this report, OCGS preoperational data was not used due to it's collection 35 years ago. Several factors were important in the interpretation of the data:
- 1.
1 ower 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 5
I 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 criteria 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 Reilts 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 effecting 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 11 nuclides, Mn-54, Co-58, Fe-59, Co-60, Zn-65, Zr-95, Nb-95, 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-134, and Cs-1 37 were reported.
For clams eight nuclides, K-40, Mn-54, Co-58, Fe-59, Co-60, Zn-65, Cs-I 34, and Cs-1 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.
For air particulate six nuclides, Be-7, Mn-54, Co-58, Co-60, Cs-134, and Cs-1 37 were reported.
For air cartridges one nuclide, 1-131 was reported.
6
For vegetation four nuclides, K-40,1-131, Cs-134, and Cs-1 37, 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 2002 the OCGS REMP had a sample recovery rate in excess of 99%.
Exceptions are listed below:
Beginning on 03 Sep 02, the charcoal cartridge efficiency (98% efficiency) on Air Iodine samples was incorporated into the analysis result. Prior to this, an efficiency of 100 % was used. All calculated MDAs were well below LLDs.
Two vegetable gardens planted at the site boundary, Stations 35 and 66, failed after the initial harvest on 06 Aug 02 due to a regional severe drought. One cabbage sample was harvested and analyzed from Station 66 on 10 Sep 02, but no other vegetables were available for collection and analysis during this collection period. Broadleaf vegetation was collected at Stations 35 and 66 in lieu of vegetable samples on 10 Sep 02 and on 10 Oct 02.
In October 2002, during the third quarter TLD change out, the field Control TLDs were lost. The Field Control dosimeters monitor the quantity of dose received during the exchange period. ICN TLD numbers 2016953 and 2016954 were lost, presumably in the field, during dosimeter exchange.
The dose recorded by the Field Control badges that is subtracted from other exposed dosimeters is usually less than 1 mR. CAP # 2003-0583 was written to investigate and document this event.
ICN TLDs were lost at Station 86 during the first quarter of 2002 and at Station 61 during the second quarter of 2002 due to vandalism.
Station 72 failed to operate after running for 12 hours1.388889e-4 days <br />0.00333 hours <br />1.984127e-5 weeks <br />4.566e-6 months <br /> and 48 minutes.
The volume of air that passed through this filter was only 58.7 cubic meters because of a blown fuse.
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 7
procedures and equipment are in place to assure reliable program implementation.
E.
Program Changes Beginning the second quarter 2002, Teledyne Brown Engineering Environmental Services became the primary laboratory and Environmental Inc. (Midwest Labs) became the QC laboratory. Prior to that, Environmental Inc. was the primary analysis laboratory and Teledyne Brown Engineering was the QC laboratory.
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:
Tritiuma 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:
8
Tritom Quarterly samples from all locations were analyzed for tritium activity (Table C-11.1, Appendix C). Tritium activity was detected in two samples at concentrations of 131 pCi/I and 166 pCi/l. The highest MDA was calculated at <178 pCiI.
Gamma Spectrometry 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 two locations (93 and 94) semiannually. Location 93 could be affected by Oyster Creek's effluent releases. The following analysis was performed:
-Gamma Spectrometry The edible portion of fish samples from two 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 3,480 to 5,900 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 1,120 to 1,420 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.
9
The edible portion of crab samples from one location was analyzed for gamma emitting nuclides (Table C-111.2, Appendix C). Naturally occurring potassium-40 was found at a concentration of 1,520 pCi/kg wet and was consistent with levels detected in previous years. No fission or activation products were found.
- 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 K-40, and the fission product Cs-1 37.
Potassium-40 was found at all stations and ranged from 806 to 16,300 pCi/kg dry. Concentrations of the fission product Cs-1 37 were found in two sediment samples. Location 23 had an average concentration of 21 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 2002.
B.
Atmospheric Environment
- 1.
Airbome
- 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 Ill represents the control and locations at a remote distance from OCGS (C and 3). The following analyses were performed:
10
Gross Beta Weekly samples were analyzed for concentrations of beta 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 On-Site locations (Group I) ranged from 9 to 34 E-3 pCi/M3 with a mean of 17 E-3 pCi/m3. The results from the Intermediate Distance location (Group II) ranged from 8 to 35 E-3 pCi/M3 with a mean of 17 E-3 pCi/e 3. The results from the Distant locations (Group l1l) ranged from 7 to 32 E-3 pCVM3 with a mean of 17 E-3 pCi/n 3. Comparison of the 2002 air particulate data with previous years data indicate no effects from the operation of OCGS (Figure C-5, Appendix C). In addition a comparison of the weekly mean values for 2002 indicate no notable differences among the three groups (Figure C-4, Appendix C).
Strohtium-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 Spectrometry 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 58 to 84 E-3 pCi/M3. 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.
11
- 2.
Terrestrial
- a.
Vegetation Samples were collected from three locations (35, 36, and 66) when available. The following analyses were performed:
Strontium-89 and Strontium-90 Vegetation samples from all locations were analyzed for concentrations of strontium-89 and strontium-90 (Table C-V11.1, Appendix C). All strontium-89 results were less than the MDA. Strontium-90 was detected in all but one sample.
The values ranged from 3 to 121 pCikg wet.
Gamma Spectrometry Each vegetation sample from locations 35, 36, and 66 were analyzed for concentrations of gamma emitting nuclides (Table C-V11.1, Appendix C).
Naturally occurring K-40 activity was found in all samples and ranged from 1,640 to 4,030 pCVI. Cs-137 activity detected in two 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 814 (CaSO4) thermoluminescent dosimeters. Forty-four TLD locations were monitored around the site. Results of TLD measurements are listed in Tables C-V111.1 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. 2002 gamma radiation data was plotted from the control location 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).
12
Land Use Survey A Land Use Survey was conducted during 2002 around the Oyster Creek Generating Station (OCGS). The purpose of the survey was to determine the location of animals producing milk for human consumption in each of the sixteen meteorological sections out to a distance of 5 miles from the OCGS. 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 Buildings Sector Residence Garden Milk Farm 1 WSW 10.1 2 SW 20.3 3NW 17.7 4 NNE 5.9 13
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 1,1982.
- 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.
14
- 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.
15
I
- 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.
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GPU Nuclear, Inc. 1999 Radiological Environmental Monitoring Report for Oyster Creek Nuclear Generating Station. May 2000.
16
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AmerGen Energy Company, LLC. 2000 Radiological Environmental Monitoring Report for Oyster Creek Generating Station. May 2001.
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AmerGen Energy Company, LLC. 2001 Radiological Environmental Monitoring Report for Oyster Creek Generating Station May, 2002.
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AmerGen Energy Company, LLC. Oyster Creek Generating Station Radioactive Effluent Release Report, January 1, 2002. through December 31, 2002. March 2003 17
Intentionally Left Blank
APPENDIX A RADIOLOGICAL ENVIRONMENTAL MONITORING REPORT
SUMMARY
TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR THE OYSTER CREEK GENERATING STATION, 2002 Name of Facility:
OYSTER CREEK GENERATING STATION DOCKET NUMBER:
50-219 Location of Facility: OCEAN COUNTY, NJ REPORTING PERIOD:
2002 INDICATOR CONTROL LOCATION WITH 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 SURFACE WATER (PCI/LITER)
TRITIUM 28 3000 147 (5/16)
(<94/327) 142 (4/12)
(<94t207) 214 (1/2)
(<101/327) 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 15 3
(0/16)
(<o 91<6) 15 4
(0/16)
(<1/<6) 15 3
(0/16)
(<0.9/<6) 30 8
(0/16)
(<2/<12) 30 7
(0/16)
(<2/<12) 30 6
(0/16)
(<2/<1 1) 15 4
(0/16)
(<1/<6) 4 (0/12)
(<1/<6) 4 (0/12)
(<1/<7) 4 (0/12)
(<1/<6) 8 (0/12)
(<2/<14) 8 (0/12)
(<2/<15) 7 (0/12)
(<2/<11) 4 (0/12)
(<I/<7) 4 (0/12)
(<1/<6) 4 (0/12)
(<c/<7) 4 (0/12)
(<1/<6) 8 (0/2)
(<51<11) 8 (0/12)
(<2/<15) 7 (0/12)
(<2/<l 1) 5 (0/2)
(<4/<6) 94 CONTROL GREAT BAYILITTLE 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 24 INDICATOR BARNEGAT BAY 2.1 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
- 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 INDICTED IN PARENTHESES (F)
TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR THE OYSTER CREEK GENERATING STATION, 2002 Name of Facility:
OYSTER CREEK GENERATING STATION DOCKET NUMBER:
50-219 Location of Facility: OCEAN COUNTY, NJ REPORTING PERIOD:
2002 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN*
MEANS 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 BA-140 LA-140 15 4
(0/16)
(<0.9/<8) 18 4
(0/16)
(<0.91<7) 60
<24 (0/16)
(<10/<45) 15 8
(0/16)
(<2/<15) 4 (0/12)
(<0.9/<7) 4 (0/12)
(<1/<6)
<26 (0/12)
(<10/<43) 7 (0/12)
(<2/<13) 4 (0/12)
(<0.9/<8) 4 (0/12)
(<11<6)
<36 (0/2)
(<271<45) 12 (0/2)
(<10/<14) 33 INDICATOR ROUTE 9 BRIDGE 0.4 MILES ESE OF SITE 94 CONTROL GREAT BAY/LITTLE EGG HARBOR 20.0 SSW OF SITE 24 INDICATOR BARNEGAT BAY 2.1 MILES SE OF SITE 23 INDICATOR BARNEGAT BAY 3.6 MILES ENE OF SITE 0
0 0
0 WELL WATER (PCI/LITER)
TRITIUM 12 2000 130 (2/8)
(<86/<178) 124 (0/4)
(<86/<178) 132 (1/4)
(<86/132) 38 INDICATOR OCEAN TOWNSHIP MUA PUMP STA 1.3 MILES SSW OF SITE 0
GAMMA MN-54 12 15 3
(0/8)
(<11<5) 4 (0/4)
(<2/<6) 4 (0/4)
(<2/<6) 37 CONTROL LACEY MUA PUMPING STATION 2 2 MILES NNE OF SITE 0
CO-58 CO-60 15 3
(0/8)
(<1/<6) 15 3
(0/8)
(<11<5) 4 (0/4)
(<2/<6) 4 (0/4)
(<2/<5) 4 (0/4)
(<2/<6) 4 (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 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 INDICTED IN PARENTHESES (F)
TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR THE OYSTER CREEK GENERATING STATION, 2002 Name of Facility:
OYSTER CREEK GENERATING STATION DOCKET NUMBER:
50-219 Location of Facility: OCEAN COUNTY, NJ REPORTING PERIOD:
2002 INDICATOR CONTROL LOCATION WITH HIGHEST 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 FE-59 ZN-65 ZR-95 w
NB-95 CS-134 CS-137 BA-140 LA-140 30 7
(0/8)
(<3/<11) 30 6
(0/8)
(<2/<1 1) 30 7
(0/8)
(<2/<10) 15 4
(0/8)
(<1/<6) 15 3
(0/8)
(<0 9/<6) 18
<3.5 (0/8)
(<11<5) 60
<22 (0/8)
(<13/<40) 15 7
(0/8)
(<4/<13) 9 (0/4)
(<S/<13) 8 (0/4)
(<4/<13) 8 (0/4)
(<6/<10)
S (0/4)
(<3/<7) 4 (0/4)
(<2/<6)
<3.6 (0/4)
(<2<6)
<32 (0/4)
(<171<45) 10 (0/4)
(<31<15) 9 (0/4)
(<51<13) 8 (0/4)
(<4/<13) 8 (0/4)
(<61<10) 5 (0/4)
(<31<7) 4 (0/4)
(<21<6)
<3.6 (0/4)
(<21<6)
<32 (0/4)
(<171<45) 10 (0/4)
(<3/<15) 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 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 37 CONTROL LACEY MUA PUMPING STATION 2.2 MILES NNE OF SITE 37 CONTROL LACEY MUA PUMPING STATION 2.2 MILES NNE 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 INDICTED IN PARENTHESES (F)
TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR THE OYSTER CREEK GENERATING STATION, 2002 Name of Facility:
OYSTER CREEK GENERATING STATION DOCKET NUMBER:
50-219 Location of Facility: OCEAN COUNTY, NJ REPORTING PERIOD:
2002 INDICATOR CONTROL LOCATION WITH 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 (PuCIKG WETr (FISH)
(PCI/KG WET)
GiAAMMA K-40 2
MN-54 CO-58 N/A 4210 (2/2)
(3480/4940) 130 33 (0/2)
(<14/<52) 130 37 (0/2)
(<201<54)
N/A NIA NIA 4210 (2/2)
(3480/4940) 33 (0/2)
(<14/<52) 37 (0/2)
(<20/<54) 93 INDICATOR DISCHARGE CANAL 0 1 MILES WSW OF SITE 93 INDICATOR DISCHARGE CANAL
- 0. I MILES WSW OF SITE 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSW OF SITE 0
0 0
CO-60 130 33 (0/2)
(<14/<53)
N/A 33 (0/2)
(<14/<53) 93 INDICATOR DISCHARGE CANAL 0 1 MILES WSW OF SITE 0
FE-59 ZN-65 260 98 (0/2)
(<54/<142) 260 71 (0/2)
(<33/<109)
N/A N/A 98 (0/2)
(<54/<142) 71 (0/2)
(<3 3/< 109) 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSW OF SITE 93 INDICATOR DISCHARGE CANAL 0 1 MILES WSW OF SITE 0
0 CS-134 130 29 (0/2)
(<13/<44)
N/A 29 (0/2)
(<13/<44) 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSW OF SITE 0
CS-137 150 33 (0/2)
(<15/<52)
N/A 33 (0/2)
(<15/<52) 93 INDICATOR DISCHARGE CANAL
- 0. I MILES WSW 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 INDICTED IN PARENTHESES (F)
TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR THE OYSTER CREEK GENERATING STATION, 2002 Name of Facility:
OYSTER CREEK GENERATING STATION DOCKET NUMBER:
50-219 Location of Facility: OCEAN COUNTY, NJ REPORTING PERIOD; 2002 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED M MEA NM 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 PREDATOR (FISH)
(PCI/KG WET)
GAMMA K-40 9
N/A 4686 (515)
(4040/5900) 4578 (4/4)
(3770/5530) 4686 (515)
(4040/5900) 93 INDICATOR DISCHARGE CANAL 0 1 MILES WSW OF SITE 0
MN-54 CO-58 CO-60 FE-59 ZN-65 CS-134 CS-137 130 19 (0/5)
(<12/<29) 130 26 (0/5)
(<15/<42) 130 18 (0/5)
(<I 1/<25) 260 63 (0/5)
(<41/<102) 260 45 (0/5)
(<27/<68) 130 18 (0/5)
(<11/<28) 150 20 (0/5)
(<I 1/<29) 25 (0/4)
(<10/<48) 35 (0/4)
(<13/<72) 24 (0/4)
(<10/<48) 97 (0/4)
(<35/<205) 56 (0/4)
(<22/<109) 24 (0/4)
(<I0/<49) 27 (0/4)
(<10/<56) 25 (0/4)
(<10/<48) 35 (0/4)
(<13/<72) 24 (0/4)
(<10/<48) 97 (0/4)
(<35/<205) 56 (0/4)
(<22/<109) 24 (0/4)
(<10/<49) 27 (0/4)
(<10/<56) 94 CONTROL GREAT BAY/LITTLE EGG HARBOR 20 0 SSW OF SITE 94 CONTROL GREAT BAY/LITrLE EGG HARBOR 20 0 SSW OF SITE 0
0 94, CONTROL GREAT BAYILITTLE 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 INDICTED IN PARENTHESES (F)
TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR THE OYSTER CREEK GENERATING STATION, 2002 Name of Facility:
OYSTER CREEK GENERATING STATION DOCKET NUMBER:
50-219 Location of Facility: OCEAN COUNTY, NJ REPORTING PERIOD:
2002 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEANS 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 CLAMS (PCI/KG WET)
GAMMA K-40 6
N/A 1328 (4/4)
(1140/1420) 1215 (2/2)
(1120/1310) 1375 (2/2)
(1340/1410) 24 INDICATOR BARNEGAT BAY 2.1 MILES SE OF SITE 0
MN-54 CO-58 CO-60 FE-59 ZN-65 CS-134 CS-137 130 17 (0/4)
(<13/<21) 130 21 (0/4)
(<16128) 130 16 (014)
(<14/<17) 260 51 (0/4)
(<34/<70) 260 36 (0/4)
(<32/<43) 130 14 (0/4)
(<I 1/<18) 150 17 (0/4)
(<15/<20) 20 (0/2)
(<14/<27) 25 (012)
(<16/<33) 17 (0/2)
(<13/<21) 56 (0/2)
(<331<79) 36 (0/2)
(<26/<47) 17 (0/2)
(<13/<22) 18 (0/2)
(<15/<22) 20 (0/2)
(<14/<27) 25 (0/2)
(<16/<33) 17 (0/2)
(<13/<21) 56 (0/2)
(<33/<79) 38 (0/2)
(<34/<43) 17 (0/2)
(<13/<22) 18 (0/2)
(<15/<22) 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 BAYILITTLE EGG HARBOR 20.0 SSW OF SITE 23 INDICATOR BARNEGAT BAY 3.6 ENE OF SITE 94 CONTROL GREAT BAYILITTLE EGG HARBOR 20.0 SSW OF SITE 94 CONTROL GREAT BAYILITTLE EGG HARBOR 20 0 SSW 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 INDICTED IN PARENTHESES (F)
TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR THE OYSTER CREEK GENERATING STATION, 2002 Name of Facility:
OYSTER CREEK GENERATING STATION Location of Facility: OCEAN COUNTY, NJ MEDIUM OR PATHWAY SAMPLED
- (UNIT OF MEASUREMENT)
TYPES OF ANALYSES PERFORMED NUMBER OF ANALYSES PERFORMED REQUIRED LOWER LIMIT OF DETECTION (LLD)
INDICATOR LOCATIONS MEANS (F)
RANGE DOCKET NUMBER:
REPORTING PERIOD:
CONTROL LOCATIC LOCATION MEAN*
MEAN*
(F)
(F)
RANGE RANGE STATION #
NAME DISTANCE AND DIRECTION 50-219 2002 IN WITH HIGHEST ANNUAL MEAN NUMBER OF NONROUTINE REPORTED MEASUREMENTS CRABS (PCI/KG WET)
GAMMA K-40 I
N/A 1520 (1/1)
(1520) 130 17 (0/1)
(<17)
N/A N/A 1520 (1/1)
(1520) 17 (0/1)
(<17) 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSW OF SITE 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSW OF SITE 0
MN-54 0
CO-58 130 26 (0/1)
(<26)
N/A 26 (0/1)
(<26) 93 INDICATOR DISCHARGE CANAL
- 0. I MILES WSW OF SITE 0
CO-60 130 15 (0/1)
(<15)
N/A 15 (0/1)
(<15) 93 INDICATOR 0
DISCHARGE CANAL 0.1 MILES WSW OF SITE FE-5s9 ZN-65 260 81 (0/1)
(<81) 260 36 (0/1)
(<36)
N/A 81 (0/1)
(<81)
N/A 36 (0/1)
(<36) 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSW OF SITE 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSW OF SITE 0
0 CS-134 CS-137 130 15 (0/1)
(<15) 150 17 (0/1)
(<17)
N/A N/A 15 (0/1)
(<15) 17 (0/1)
(<17) 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSW OF SITE 93 INDICATOR DISCHARGE CANAL 0.1 MILES WSW 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 INDICTED IN PARENTHESES (F)
TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR THE OYSTER CREEK GENERATING STATION, 2002 Name of Facility:
OYSTER CREEK GENERATING STATION DOCKET NUMBER:
50-219 Location of Facility: OCEAN COUNTY, NJ REPORTING PERIOD:
2002 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 LOWER LIMIT (F)
(F)
(F)
NAME NONROUTINE (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT)
(LLD)
MEASUREMENTS SEDIMENT (PCI/KG DRY)
GAMMA K.40 8
N/A 6396 (6/6)
(806/16300) 8290 (2/2)
(2580/14000) 9365 (2/2)
(2430/16300) 23 INDICATOR BARNEGAT BAY 3.6 MILES ENE OF SITE 0
MN-54 CO-58 CO-60 CS-134 CS-137 N/A 11 (0/6)
(<6/<18)
N/A 12 (0/6)
(<6/<20)
N/A 11 (0/6)
(<5/<20) 150 10 (0/6)
(<5/<16) 180 13 (2/6)
(<6/26) 10 17 (312/312)
(7/35) 20 (0/2)
(<17/<22) 23 (0/2)
(<18/<28) 18 (0/2)
(<17/<20) 17 (0/2)
(<14/<20) 20 (0/2)
(<16/<24) 18 (52/52)
(9/32) 20 (0/2)
(<17/<22) 23 (on)
(<18/<28) 18 (0/2)
(<17/<20) 17 (0/2)
(<14/<20) 21 (2/2)
(16/26) 18 (52/52)
(9134) 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 23 INDICATOR BARNEGAT BAY 3 6 MILES ENE OF SITE 20 INDICATOR FINNINGER FARM 0.7 MILES E OF SITE 0
0 0
0 0
0 AIR PARTICULATE (E-3 PCI/CU.METER)
GROSS BETA 364 SR-89 28 N/A 2.7 (0/24)
(<0.2/<6.6) 2.6 (0/4)
(<0.2<5.5) 3.2 (0/4)
(<0.2/<6 6) 66 INDICATOR OCGS DISCHARGE CANAL 0.4 MILES SE 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 INDICTED IN PARENTHESES (F)
TABLE A-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR THE OYSTER CREEK GENERATING STATION, 2002 Name of Facility:
OYSTER CREEK GENERATING STATION DOCKET NUMBER:
50-219 Location of Facility: OCEAN COUNTY, NJ REPORTING PERIOD:
2002 INDICATOR CONTROL LOCATION WITH 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 SR-90 GAMMA BE-7 MN-54 CO-58 CO-60 CS-134 CS-137 28 28 364 NIA 1.3 (0/24)
(<O.1/<4.4)
N/A 71 (24/24)
(60/84)
N/A 0 4 (0/24)
(<0.2/<1.0)
N/A 0.5 (0/24)
(<0 V<1.3)
N/A 0.5 (0/24)
(<0.2/<1.2) 50 04 (0/24)
(<021<O 8) 60 04 (0/24)
(<0,I/<O 9) 70 8
(0/312)
(<11<119) 4.7 (0/4)
(<0.11<15) 64 (4/4)
(58/67) 03 (014)
(<0 21<0.3) 0.4 (0/4)
(<0.21<O 4) 03 (0/4)
(<o 31<0.5) 0.3 (0/4)
(<0.2/<0.3) 03 (0/4)
(<0 2/<0.3) 7 (0/52)
(<11<36) 4.7 (0/4)
(<0.11<15) 79 (4/4)
(76/84) 0.5 (0/4)
(<0.31<1.0) 06 (0/4)
(<0.21<1.3) 06 (0/4)
(<0.4/<1.2) 0.5 (0/4)
(<0 3/<0 8) 05 (0/4)
(<0.21<0.9) 10 (0/52)
(<21<119)
C CONTROL GPU ENERGY OFFICE 24.7 MILES NW OF SITE 20 INDICATOR FINNINGER FARM 0.7 MILES E 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 66 INDICATOR OCGS DISCHARGE CANAL 0.4 MILES SE OF SITE 66 INDICATOR OCGS DISCHARGE CANAL 0.4 MILES SE OF SITE 72 INDICATOR LACEY ROAD 1.9 MILES NNE OF SITE 0
0 0
0 0
0 0
AIR IODINE (E-3 PCI/CU METER) 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 INDICTED IN PARENTHESES (F)
TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR THE OYSTER CREEK GENERATING STATION, 2002 Name of Facility:
OYSTER CREEK GENERATING STATION DOCKET NUMBER:
50-219 Location of Facility: OCEAN COUNTY, NJ REPORTING PERIOD:
2002 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN*
MEANS 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 VEGETATION (PCI/KG WET)
SR-89 16 16 SR-90 N/A 23 (0/9)
(<31<64)
N/A 32 (7/9)
(3/121)
N/A 2804 (9/9)
(1640/4030) 14 (0/7)
(<7/<25) 68 (7n)
(3/12) 4340 (7/7)
(2790/6860) 32 (0/4)
(<12/<64) 41 (3/4)
(<38/84) 4340 (717)
(2790/6860) 35 INDICATOR OCGS DISCHARGE CANAL 0.4 MILES ESE OF SITE 35 INDICATOR OCGS DISCHARGE CANAL 0.4 MILES ESE OF SITE 35 INDICATOR OCGS DISCHARGE CANAL 0 4 MILES ESE OF SITE 0
0 I0 GAMMA K-40 16 0
1-131 CS-134 CS-137 60 358 (0/9)
(<28/<1150) 60 26 (0/9)
(<7/<49) 80 30 (2/9)
(<91<47) 168 (0/7)
(<23/<400) 11 (0/7)
(<6/<22) 1 1 (0/7)
(<6/<23) 467 (0/4)
(<621<1150) 33 (0/4)
(<18/<49) 37 (1/4)
(28/<47) 35 INDICATOR OCGS DISCHARGE CANAL 0 4 MILES ESE OF SITE 35 INDICATOR OCGS DISCHARGE CANAL 0 4 MILES ESE OF SITE 35 INDICATOR OCGS DISCHARGE CANAL 0.4 MILES ESE OF SITE 0
0 0
DIRECT RADIATION TLD-QUARTERLY (MILLI-ROENTGEN/STD QUARTER 174 N/A 12.4 (166/166)
(6.7/21 6) 12.7 (8/8)
(11.0/14.8) 19.9 (4/4)
(18.4/21.6) 55 INDICATOR OCGS SWITCHYARD 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 INDICTED IN PARENTHESES (F)
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 = Air Particulate AIO
= Air Iodine WWA = Well Water VEG
= Vegetation SWA = Surface Water AQS = 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 that 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, 2002 Sample TLD WWA APT, AIO, TLD TLD TLD TLD APT. AIO, TLD TLD TLD APT, AIO TLD SWA, CLAM, AQS SWA, CLAM, AQS SWA, AQS, FISH VEG VEG WWVA WWA TLD TLD Station Distance Azimuth 1
0.4 1
01 02 3
60 6
2.1 8
2.3 9
20 C
247 11 82 j
14 20 8 20 07 22 16 23 36 24 2.1 33 0.4 35 04 36 23.1 37 2.2 38 16 51 04 52 03 (degrnesn 219 209 349 97 13 177 230 313 152 2
95 145 64 101 123 111 319 18 197 358 333 DP-triptin 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 NNE of site, Lane Place, behind St. 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, GPU Energy office in rear parking lot, Cookstown.
NJ SSE of site, 80" 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 LUght 1' East of site, Bamegat Bay, approximately 250 yards SE of
'Flashing Light 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 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 B-2
TABLE B-2:
Radiological Environmental Monitoring Program - Sampling Locations, Distance and Direction, Oyster Creek Generating Station, 2002 Sample Madillm TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD APT, APO, TLD.
VEG TLD APT, AlO, TLD APT, A1O, TLD APT, AlO, TLD TLD Station Cnda 53 54 55 56 57 58 59 61 62 63 64 65 66 68 71 72 73 74 Distance Azimuth 0miiP3) 03 03 03 03 02 0 2 03 0.3 02 02 0.3 04 04 1.3 1 6 1 9 1.8 1.8 20 1.8 309 288 263 249 206 188 166 104 83 70 48 19 133 265 164 25 108 88 nDasrrpIon 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 secunty 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 Main 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 Bndge, Forked River, NJ SE of site, east of Route 9 and south of the OCGS Discharge Canal, Inside fence, Waretown, NJ West of site, on Garden State Parkway at mile marker 71.7.
Lacey Township, NJ SSE of site, on Route 532 at the Waretown Municipal Building. Waretown, NJ 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 TLD 75 71 ENE of site, Beach Blvd. and Maui Drive, Forked River, NJ 2
North of site, 1514 Anent Road, Forked River, NJ TLD 78 B-3
TABLE B-2:
Radiological Environmental Monitoring Program - Sampling Locations, Distance and Direction, Oyster Creek Generating Station, 2002 Sample Mpzilm TLD TLD Station 79 81 Distance 29 3.5 44 Azimuth 160 SSE of site, Hightide Drive and Bonita Drive, Waretown, NJ 201 SSW of site, on rose Hill Road at intersection with Bamegat Boulevard, Bamegat, NJ 36 NE of site, Bay Way and Clairmore Avenue, Lanoka Harbor, NJ TLD 82 TLD 84 TLD 85 TLD 86 4.4 39 50 66 6.1 6.3 90 TLD TLD TLD TLD 88 89 90 92 332 NNW of site, on Lacey Road, 1 3 miles west of the Garden State Parkway on siren pole, Lacey Township, NJ 250 WSW of site, on Route 532, just east of Wells Mills Park, Waretown, NJ 224 SW of site, on Route 554, 1 mile west of the Garden State Parkway, Bamegat, NJ 125 SE of site, eastern end of 3Pd Street, Bamegat Light, NJ 108 ESE of site, Job Francis residence, Island Beach State Park 75 ENE of site, parking lot A-5, Island Beach State Park 46 NE of site, at Guard Shack/Toll Booth, Island Beach State Park 242 WSW of site, OCGS Discharge Canal between Pump Discharges and Route 9, Forked River, NJ 198 SSW of site, in Great BaylLittle Egg Harbor 292 WNW of site, on Garden State Parkway at mile marker 72 3, Lacey Township, NJ FISH, CRAB SWA, AQS, CLAM, FISH TLD 93 0.1 94 20 0 98 1.3 TLD 99 1 5 0.4 310 NW of site, on Garden State Parkway at mile marker 72 8, Lacey Township, NJ 219 SW of site, at OCGS Fire Pond, Forked River, NJ TLD T1 B4
TABLE B-3:
Radiological Environmental Monitoring Program - Summary of Sample Collection and Analytical Methods, Oyster Creek Generating Station, 2002 Sample Analysis Sampling Method Collection Procedure Number Sample Size Analytical Procedure Number Medium Surface Water Gamma Spectroscopy Grab Sample.
2120-IMP4522.06 Oyster Creek sample 1 gallon TBE, PRO-042-5 Determination of gamma emitting collection procedure - surface water radioisotopes RMC-ER5 Collection of water samples for Env. Inc., GS-01 Determination of gamma emitters by radiological analysis (Oyster Creek Generating gamma spectroscopy Station)
Surface Water Tritium Grab Sample.
2120-IMP-4522.06 Oyster Creek sample 1 gallon TBE, PRO-052-35 Determination of tntium in water by liquid collection procedure - surface water scintiilation RMC-ER5 Collection of water samples for Env. Inc., T-02 Determination of tntium In water (direct radiological analysis (Oyster Creek Generating method) station)
Well Water Gamma Spectroscopy Monthly samples 2120-IMP-4522.10 Oyster Creek sample 1 gallon TBE, PRO-042-5 Determination of gamma emitting composited quarterly.
collection procedure - well water radioisotopes Env. Inc., GS-01 Determination of gamma emitters by gamma spectroscopv 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 tntium in water (direct method)
Fish Gamma Spectroscopy Semi-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 line technique and traps RMC-ER6 Collection of fish samples for Env. Inc., GS-01 Determination of gamma emitters by radiological analysis (Oyster Creek Generating gamma spectroscopy Station)
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 - dams and crabs radioisotopes clam tongs and traps.
RMC-ER6 Collection of fish samples for Env. Inc. GS-01 Determination of gamma emitters by radiological analysis (Oyster Creek Generating gamma spectroscopy Station)
Sediment Gamma Spectroscopy Semi-annual grab 2120-IMP4522.03 Oyster Creek collection 1000 grams (dry)
TBE, PRO-042-5 Determination of gamma emitting samples procedure - aquatic sediment radioisotopes RMC-ER7 Collection of sediment samples for Env. Inc. GS-01 Determination of gamma emitters by radiological analysis (Oyster Creek Generating gamma spectroscopy I Station)
B-5
TABLE B-3:
Radiological Environmental Monitoring Program - Summary of Sample Collection and Analytical Methods, Oyster Creek Generating Station, 2002 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 1 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 carticulate 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 snectroscopv Air Particulates Strontium-89/90 Quarterly composite of 2120-IMP-4522 05 Oyster Creek sample 13 filters TBE, PRO-032-24R Determination of radiostrontium 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 spectroscopy (batch method)
Vegetation Gamma Spectroscopy Grab sample dunng 2120-IMP-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 spectroscopy Vegetation Stronbum-89/90 Grab sample during 2120-IMP-4522.04 Oyster Creek sample 1000 grams TBE, PRO-032-23R Determination of radiostrontium in growing season.
collection procedure - food products and feedstuff and forage broadleaf veaetables TLD Thermoluminescence Quarterly TLDs 2120-IMP-4522.02 Oyster Creek sample 2 dosimeters ICN Pharmaceutical Dosimetry comprised of two collection procedure - Thermoluminescent Panasonic 814 Dosimetry (containing 3 each CaSO4 elements)
B-6
v'r 24 Barnegat Bay Figure B-1 Oyster Creek Generating Station (O CGS)
Locations of Radiological Fvironnental Monitoring Prgran (REMF)
Stations wiffin two miles oftthe OCGS B-7
Atlantic Ocean Figure B-2 Oyster Creek Generating Station (OCGS)
Locations of Radiological Environnmntal Mo~nitoring Program (REMP)
Stations greater tn 2 miles ifom the OCGS 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, 2002 RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMA COLLECTION PERIOD 23 24 33 94 JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC
< 102
< 162
< 101 327 +/- 87 214 +/- 320
< 113
< 94
< 98 138 +/- 65
< 106 95 +/- 60 160 +/- 83 195 +/- 77
< 121
< 159
< 183
< 194 138 +/- 78
< 113
< 94
< 99 114 +/- 63
< 107
< 95 207 +/- 84 196 +/- 79 125 +/- 77
< 169
< 189
< 191 142 +/- 89 MEAN*
132 +/- 85
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES C-1
TABLE C-1.2 CONCENTRATIONS OF GAMMA EMITTERS IN SURFACE WATER SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2002 RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMA STC COLLECTION DUD Inm Mn-54 Co-58 Fe-59 Co-60 Zn-65 Zr-95 Nb-95 Cs-134 Cs-1 37 Ba-140 La-140 rcrl~luu 23 JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC
<4
< 2
< 5
< 10
< 4
< 9
< 8
< 5
<6
<4
< 4
< 2
< 41
< 32
< 14
< 10
< 6
< 5
< 4
< 2 MEAN*
r4) 24 JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC 3 +/-
3 4 +/- 3 8 +/- 5 3 +/-
3 7 +/-
7 6 +/- 4 5 +/-
3 3 +/- 3 3 +/- 3 36 +/-
12 12 +/- 6
< 4
< 11
<4
< 10
< 4
<8
<6
<4
<3
< 4
< 2
< 4
< 2
< 45
< 27
< 15
< 9
< 2
< 2 MEAN*
3 +/- 3 4 +/- 4 8 +/- 8 3 +/- 4 7 +/- 9 6 +/- 7 4 +/- 4 3 +/- 4 3 +/- 3 36 +/- 26 12 +/- 9
- 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, 2002 RESULTS IN UNITS OF PCI/LITER +/- 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 Cs-134 Cs-137 Ba-140 La-140
< 3
< 5
< 6
< 5
< 6
< 4
< 3
< 2
< 0.9
< 2
< 2
<2
<5
<6
<5
<6
< 4
< 4
< 2
< 1
< 2
< 2
< 4
< 6
< 8
< 12
< 12
< 11
< 9
< 8
< 4
< 2
< 6
< 9
< 3
< 6
< 5
< 5
< 5
< 4
< 3
< 1
< 0.9
< 2
< 3
< 4
< 4
< 10
< 12
< 11
< 12
< 8
< 7
< 3
< 2
< 4
< 8
< 6
< 11
< 9
< 9
< 9
< 8
< 6
< 3
< 2
< 4
< 3
< 4
< 3
< 3
< 3
< 6
< 8
< 6
< 6
< 6
< 5
< 6
< 6
< 5
< 4
< 4
< 3
< 2
< 1
< 1
< 09
< 2
< 2
< 2
< 2
< 4
< 2
< 5
< 6
< 7
< 6
< 4
< 4
< 2
< 0.9
< 2
< 2
< is
< 11
< 11
< 29
< 40
< 26
< 26
< 24
< 17
< 10
< 21
< 11
< 2
< 2
< 3
< 9
< 13
< 8
< 8
< 7
< 6
< 3
< 7
< 3 MEAN*
3 +/-3 3 +/-3 7 +/-6 3 +/-3 7 +/-7 6 +/-6 4 +/-4 4 +/-4 4 +/-4 20 +/-18 6 +/-7 w94 JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC
< 2
< 4
< 3
< 6
< 3
< 6
< 4
< 6
< 2
< 4
< 1
< 2
< 1
< 4
< 4
< 6
< 3
< 6
< 5
< 7
< 2
< 4
< 1
< 2
< 6
< 6
< 8
< 12
< 7
< 12
< 10
< 14
< 5
< 10
< 2
< 5
< 3
< 5
< 4
< 4
< 3
< 8
< 5
< 13
< 3
< 6
< 6
< 14
< 4
< 9
< 6
< 15
< 2
< 4
< 4
< 8
< 1
< 2
< 2
< 4
< 4
< 6
< 6
< 10
< 6
< 10
< 8
< 11
< 3
< 9
< 2
< 4
< 3
< 3
< 6
< 6
< 4
< 6
< 5
< 7
< 2
< 5
< 1
< 3
< 3
< 3
< 4
< 7
< 3
< 7
< 4
< 6
< 2
< 3
< 0.9
< 2
< 4
< 5
< 4
< 6
< 3
< 6
< 4
< 6
< 2
< 4
< 1
< 2
< 18
< 22
< 30
< 30
< 26
< 30
< 26
< 38
< 18
< 43
< 10
< 16
< 2
< 3
< 7
< 9
< 9
< 9
< 9
< 13
< 6
< 13
< 3
< 5 MEAN' 4 +/-4 4 +/-4 8 +/-7 4 +/-3 8 +/-9 7 +/-6 4 +/-4 4 +/-4 4 +/-3 26 +/-19 7 +/-7
- 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, 2002 RESULTS IN UNITS OF PCI/LITER + 2 SIGMA COLLECTION PERIOD 1
37 38 JAN - MAR APR - JUN JUL - SEP OCT - DEC MEAN*
131 +/- 55
< 98
< 131
< 151
< 86
< 97
< 133
< 178
< 86
< 97 166 +/- 86
< 178 128 +/- 44 124 +/- 83 132 +/- 94
' 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, 2002 RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMA STC COLLECTION PERIOD Mn-54 Ca-58 Fe-59 Co-60 Zn-65 Zr-95 Nb-95 Cs-134 Cs-137 Ba-140 La-140 I
JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC MEAN'
< 5
< 4
< 5
< 4
< 5
< 10
< 4
< 3
< 4
< 14
< 3
< 3
< 8
< 3
< 6
< 6
< 4
< 3
< 3
< 23
< 5
< 8
< 5
< 5
< 11
< 5
< 11
< 9
< 6
< 6
< 5
< 40
< 13 3 +/-3 4+/-t3 7+/-t7 3+/-t3 6 +/-7 7 +/-6 4 +/-4 3+/-t4 4 +/-3 22 +/-25 8+/- 8 C-0t 37 JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC MEAN'
< 2
< 2
< 5
< 2
< 4
< 7
< 3
< 4
< 2
< 17
< 3
< 4
< 5
< 10
< 4
< 9
< 8
< 5
< 4
< 4
< 31
< 6
< 6
< 13
< 5
< 13
< 10
< 7
< 5
< 6
< 45
< 3
< 3
< 8
< 3
< 6
< 6
< 4
< 2
< 3
< 34
< 11
< 15
<12 4+/-i3 4+/-t4 9 +/-7 4 +/-3 8 +/-8 8 +/-4 5+/-t4 4 +/-3 4+/-i3 32 +/-23 10 +/-10
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES
I )
TABLE C-11.2 CONCENTRATIONS OF GAMMA EMITTERS IN WELL WATER SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2002 RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMA STC COLLECTION n--Ir-Mn-54 Co-58 Fe-59 Co-60 Zn-65 Zr-95 Nb-95 Cs-134 Cs-137 Ba-140 La-140 UtK~iuu 38 JAN FEB MAR APR MAY JUN JUL AUG SEP OCT 0
- 0)
<4
<3
<6
<4
<3
<4
<7
<3
<4
< 5
< 10
< 4
<1
<1
<7
<2
< 4
< 10
< 6
< 4
< 5
< 15
< 7
< 6
< 4
< 3
< 3
< 24
< 6
< 8
< 10
< 8
< 5
< 5
< 5
< 35
< 11
< 4
< 2
< 1
< 1
< 1
< 14
< 4 MEAN*
3 +/- 3 3 +/- 3 7
- 3 3 +/- 2 6 +/- 5 6 +/- 6 4 +/- 4 3 +/- 3 4 +/- 3 22 +/- 19 7 +/- 6
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES
TABLE CI111.1 CONCENTRATIONS OF GAMMA EMITTERS IN PREDATOR & BOTTOM FEEDER (FISH)
SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2002 RESULTS IN UNITS OF PCI/KG WET +/- 2 SIGMA STC COLLECTION PERIOD K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 Cs-134 Cs-137 93 PREDATOR 04/15 -
04/15 -
09/10 09/11 09/12
- 04/15/02 I 04/15/02 09/10/02 09/11/02 09/12102 4650 +/- 344 4040 +/- 306 4750 i 421 4090 +/- 438 5900 i 486
< 17
< 14
< 12
< 29
< 25
< 18
< 17
< 15
< 42
<36 26 +/- 25
< 54
< 20
< 40
< 41
< 43
< 102
< 90 63 +/- 60
< 142
< 54
< 16
< 15
< 11
< 25
< 24 18 +/- 12
< 53
< 14
< 41
< 34
< 27
<68
< 56 45 +/- 34
< 109
< 33
< 14
< 13
< 11
< 28
< 21 18 +/- 14
< 17
< 16
< 11
<29
< 25 20 +/- 14 MEAN*
4686 +/- 1501 19 t 14 93 BOTTOM FEEDER 04/18 - 04/18/02 3480 +/- 724
< 52 09/12 09/12/02 4940 t 481
< 14
< 44
< 13
< 52
< 15 MEAN*
4210 +/- 2065 33 +/- 53 37 +/- 49 98 +/- 125 33 +/- 56 71
+/- 108 29 +/- 43 33 +/- 53 94 PREDATOR 10/04 -
10/04 -
10/04 -
10/04 -
10/04/02 10/04/02 10/04/02 10/04/02 3770 +/- 298 5530 +/- 447 4380 t 377 4630 +/- 823
< 16
< 25
< 10
< 48
< 21
< 34
< 13
< 72
< 61
< 85
< 35
< 205
< 15
< 24
< 10
< 48
< 37
< 57
< 22
< 109
< 14
< 22
< 10
< 49
< 15
< 24
< 10
< 56 MEAN' 4578 +/- 1461 25 +/- 33 35 +/- 53 97 +/- 150 24 +/- 34 56 t 76 24 +/- 35 27 +/- 42
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES
TABLE C-111.2 CONCENTRATIONS OF GAMMA EMITTERS IN CLAM AND CRAB SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2002 RESULTS IN UNITS OF PCI/KG WET +/- 2 SIGMA STC COLLECTION
,n K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 Cs-134 Cs-1 37 Vt:KIULJ 23-CLAMS 04/16 - 04/16/02 09/10 - 09/10/02 1420 +/- 220 1140 t 292
< 16
< 21
< 16
< 28 22 +/- 16
< 40
< 70 55 +/- 41
< 16
< 17 16 +/- 2
< 34
< 43 38 +/- 13
< 14
< 18
< 16
< 20 18 +/- 5 MEAN*
1280 +/- 396 18 +/- 7 16 +/- 6 24 CLAMS 04/16 - 04/16/02 09/10 - 09/10/02 1410 +/- 238 1340 +/- 255
< 13
< 17
< 16
< 22
< 34
< 62
< 14
< 16
< 32
< 36
< 11
< 15
< 15
< 16 MEAN*
1375 +/- 99 15 +/- 4 19 +/- 9 48 +/- 40 15 +/- 3 34 t 6 13 +/- 5 16 +/- 1 0,
94 CLAMS 04/17 - 04/17/02 09/12 09/12/02 1310 +/- 210 1120 +/- 250
< 14
<27
< 16
<33
< 33
< 79
< 13
< 21
< 26
< 47
< 13
< 22
< 15
< 22 MEAN' 1215 +/- 269 20 i 19 25 +/- 24 56 +/- 65
< 81 17 t 11
< 15 36 +/- 30
< 36 17 +/- 12 18 +/- 10 93 CRABS 04/18 - 04/18/02 1520 +/- 236
< 17
< 26
< 15
< 17
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES
TABLE C-IV.1 CONCENTRATIONS OF GAMMA EMITTERS IN SEDIMENT SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2002 RESULTS IN UNITS OF PCI/KG DRY +/- 2 SIGMA STC COLLECTION PERIOD Be-7 K-40 Mn-54 Co-58 Co-60 Cs-1 34 Cs-137 23 1
04/16/02 09/10/02
< 131 2430 i 227
< 182 16300 +/- 455
< 13
< 18 16 +/- 8
< 13
< 20 17 +/- 9
< 13
< 20 16 +/- 9
< 11
< 16 13 i 7 16 +/- 10 26 +/- 17 21 +/- 15 MEAN*
157 +/- 72 9365 +/- 19615 24 04/16/02 09/11/02 MEAN*
CD (0
33 04/16/02 09/11/02
< 98
< 96 97 +/- 3
< 113
< 57 85 +/- 79
< 162
< 280 806 t 148 14600 +/- 455 7703 +/- 19508 2990 +/- 211 1250 +/- 222 2120 +/- 2461 14000 +/- 420 2580 +/- 366
< 10
<9 10 +/- 2
< 12
<6 9 +/- 8
< 17
< 22
< 11
< 10 10 +/- 1
< 12
< 6 9 +/- 10
< 18
< 28
< 10
< 8 9 +/-2
< 11
< 5 8 +/- 8
< 17
< 20 9 +/- 2
< 9
< 8
< 10
< 10 10 +/- 0
< 11
< 5
< 12
< 6 MEAN*
8 +/- 8 9 +/- 10 94 04/17/02 09/12/02
< 14
< 20
< 16
< 24 MEAN' 221
+/- 167 8290 +/- 16150 20 +/- 7 23 +/- 14 18 +/- 4 17 +/- 8 20 +/- 10
- 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, 2002 RESULTS IN UNITS OF E-3 PCI/CU METER +/- 2 SIGMA GROUP I GROUP II GROUP III WEEK 20 66 71 72 73 C
3 1
28+/-1 25+/-1 27 +/- 1 21+/-1 24 +/- 1 26+/-1 27 1
2 24+/-2 26+/-3 25+/-2 28+/-2 26+/-2 27 +/-2 26 2
3 25 +/- 2
- 32 +/- 3 25 +/- 2 25 +/- 2 25 +/- 2 27 +/- 2 25 +/- 2 4
17+/-2 12+/-1 15+/-2 17+/-2 15 +/- 2 16+/-2 15 2
5 19+/-2 19+/-2 21+/-2 19+/-2 17 +/- 2 18+/-2 19 2
6 29+/-2 28+/-2 26+/-2 26+/-2 19+/-2 28+/-2 28 2
7 17+/-2 16+/-2 17+/-2 15+/-2 16+/-2 15+/-2 16 2
8 18+/-2 17+/-2 18+/-2 18+/-2 16+/-2 18+/-2 15 2
9 19+/-2 19+/-2 17+/-2 19+/-2 17 +/- 2 19+/-2 18 2
10 26+/-2 27+/-2 25+/-2 24+/-2 24 +/- 2 24+/-2 26 2
11 16+/-2 16+/-2 17+/-2 16+/-2 23+/-2 16+/-2 16 2
12 20+/-2 20+/-2 19+/-2 20+/-2 20+/-2 21+/-2 20 2
13 14+/-2 14+/-2 13+/-2 15+/-1 13+/-1 15+/-1 15 1
14 15+2 16+/-2 16+/-2 14+/-2 16 +/- 2 14+/-2 16 2
15 16+/-2 14+/-2 14+/-1 14+/-2 13+/-1 14+/-2 13 1
16 19+/-2 17+/-2 19+/-2 19+/-2 16+/-2 18+/-2 18 2
17 15+/-2 15+/-2 14+/-2 15+/-2 15 +/- 2 1 1+/-1 13 2
18 15+/-2 14+/-2 12 +/- 1 14+/-2 14+/-1 14+/-2 15 2
19 15+/-2 15+/-2 15+/-2 13+/-2 15+/-2 13+/-1 12 2
20 15+/-2 14+/-2 15+/-2 13+/-2 13+/-2 13+/-1 10 1
21 12+/-1 12+/-2 12 +/- 1 12+/-1 12+/-1 1 1+/-I1 10 1
22 17+/-2 17+/-2 18+/-2 30+/-15 (1) 18+/-2 16+/-2 17 2
23 10+/-1 11+/-2 10 +/- 1 10+/-2 9+/-1 9+/-1 10 1
24 9+/-1 10+/-2 10 +/-I 1 9+/-1 10+/-1 9+/-1 8
1 25 15+/-1 15+/-2 15 +/- 1 14+/-1 15+/-1 17+/-1 17 2
26 18+/-2 16+/-2 17+/-2 18+/-2 16+/-2 18+/-2 16 2
27 34+/-3 29+/-3 29 2
35+/-3 28+/-2 32+/-3 29 3
28 14+/-2 15+/-2 18 +/- 2 15+/-2 14+/-2 15+/-2 15 2
29 24 2
25+/-2 23 2
25+/-2 22 +/- 2 26+/-2 24 2
30 11 2
12+/-2 13 2
12+/-2 10 +/- 2 14+/-2 13 2
31 25 2
23+/-2 27 2
25+/-2 23 +/- 2 28+/-2 25 2
32 14 1
14+/-2 13 +/- 1 14+/-1 13+/-1 14i1 13 1
33 21 2
18+/-2 21 2
23+/-2 19+/-2 23i2 18 2
34 17 2
14+/-2 17 2
18+/-2 17+/-2 20+/-2 14 2
35 10 1
10+/-1 9
1 8+/-1 9+/-1 10+/-1 7
1 36 16 2
15+/-2 15 2
15+/-2 15 +/- 2 18+/-2 15 2 37 15 1
14+/-2 15 1
14+/-1 12+/-1 17+/-2 15 1
38 20 3
16+/-3 19 2
18+/-2 17+/-2 18+/-2 16 2
39 19 3
15+/-3 17 3
16+/-3 14+/-2 18+/-3 14 3
40 28 3
25+/-3 24 3
28+/-3 22+/-3 22+/-3 26 3
41 13 2
10+/-1 11 +/- 1 12+/-1 11+/-1 9+/-1 10 1
42 14 2
12+/-2 13 2
13+/-2 11+/-2 14+/-2 13 2
43 15 2
17+/-3 15 2
15+/-2 14+/-2 14+/-2 14 2
44 17 2
13+/-2 13 7
15+/-2 11+/-2 17+/-2 14 2
45 24 3
23+/-3 22 3
23+/-3 22+/-3 25+/-3 24 3
46 17 2
14+/-2 15 2
14+/-2 11t2 14+/-2 11 2 47 17 2
18+/-3 20 2
18+/-2 17+/-2 20+/-2 17 2
48 17 2
18+/-2 17 2
19+/-2 17+/-2 18+/-2 15 2
49 17 2
18+/-2 16 2
19+/-2 19+/-2 18+/-2 18 2
50 14 2
14+/-3 14 2
13+/-2 15 +/- 3 13+/-2 11 2
51 13 2
14+/-2 14 2
15+/-2 12+/-2 14+/-2 13 2
52 15 2
14+/-2 14 2
15+/-2 15+/-2 15+/-2 15 2
MEAN*
18 +/-10 17 10 17 i 10 18 +/-11 16+/-9 18 +/-11 17 11 (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, 2002 GROUP I - ON-SITE LOCATIONS GROUP Il - INTERMEDIATE DISTANCE LOCATIONS GROUP II[ -CONTROL LOCATIONS COLLECTION PERIOD 12/31/01 - 02/04/02 02104/02 - 03/04/02 03/04/02 - 04/01/02 04/01/02 - 04/29/02 04/29/02 - 06/03/02 06/03/02 - 07/01/02 07/01/02 - 08/05/02 08/05/02 - 09/02102 09/02102 - 09/30/02 09/30/02 - 11/04/02 11/04/02 - 12/02/02 12102102 - 12130/02 12/31/01 - 12130/02 MIN.
MAX.
MEAN +/-
2 SD*
12 32 24+/- 13 16 29 20+/- 10 14 27 19 +/- 9 14 19 16 +/- 3 12 15 14 +/- 3 9
18 14 +/-7 11 34 20+/- 17 14 25 18 +/- 8 10 20 15 +/- 6 10 28 17+/- 13 13 24 18+/- 8 13 18 15 +/- 4 9
34 17 +/-6 COLLECTION PERIOD MIN.
MAX.
MEAN+/-
2 SD*
12/31/01 02/04/02 03/04/02 04/01/02 04/29/02 06/03/02 07/01/02 nA/ns/nAw UJutIul
- 03/04/02
- 04/01/02
- 04/29/02
- 06/03/02
- 07/01/02
- 08/05/02 08/05/02 - 09/02102 09/02102 - 09/30/02 09/30/02 - 11/04/02 11/04/02 - 12102102 12102102 - 12130/02 15 28 23 +/- 9 15 26 19 t 7 13 25 19 +/- 8 13 19 15 t 4 12 15 13 +/- 2 9
30 15 +/- 11 10 35 20 +/- 16 13 27 19 +/- 9 8
19 14 +/- 7 11 28 16 +/- 12 11 23 17 +/- 8 12 19 16 +/- 5 8
35 17+/-6 COLLECTION PERIOD 12131/01 - 02/04/02 02104/02 - 03/04/02 03/04/02 - 04/01/02 04/01/02 - 04/29/02 04/29/02 - 06/03/02 06/03/02 - 07/01/02 07/01/02 - 08/05/02 08/05/02 - 09/02102 09/02102 - 09/30/02 09/30/02 - 11/04/02 11/04/02 - 12102102 12102102 - 12130/02 12V31/01 - 12V30/02 MIN MAX.
MEAN +/-
2 SD*
I P
A _
A j lb 27 24 +/- 10 15 28 20 +/- 11 15 26 19 +/- 8 11 18 15 +/- 5 10 15 12 +/- 3 8
18 14 +/- 8 13 32 21 +/- 15 13 28 19 +/- 11 7
18 15 +/- 7 9
26 15 +/- 11 11 25 18 +/- 10 11 18 15 +/- 5 7
32 17 +/- 7 12V31/01 - 12V30/02 10
- 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, 2002 RESULTS IN UNITS OF E-3 PCIICU METER +/- 2 SIGMA COLLECTION STC PERIOD 3
12131101 - 03/25/02 03/25/02 - 07/01/02 07/01102 - 09/30/02 09130/02 - 12V30102 COLLECTION PERIOD Sr-89
< 0 2
< 04
< 3 7
< 5 2 Sr-90
< 02
< 0 1
< 1 4
< 3.1 STC 72 12/31/01 03/25/02 07/01/02 09/30102
- 03/25/02
- 07/01/02
- 09/30/02
- 12/30/02 Sr-89
< 0.3
< 10
< 4 0
' 5 6 Sr-90
< 0.2
< 0.3
< 1.0
< 3.6 MEAN' 2.4 +/- 4.9 1.2 +/- 2 8 MEAN*
2.7 +/- 50 1.3 +/- 3.2 20 12131/01 03/25/02 07/01/02 09/30/02
- 03/25/02
- 07/01/02
- 09130/02
- 12/30/02
< 0 2
< 0 5
< 4 4
< 56
< 01
< 0.1
< 1.0
< 3 3 73 12/31/01 - 03/25/02 03/25/02 - 07/01/02 1 07/01/02 - 09/30/02 09/30/02 - 12/30/02
< 0.2
< 0.7
< 4 3
< 5.7
< 01
< 0 2
< 1.0
< 3.4 MEAN' 2.7 +/- 55 1.1 +/- 30 MEAN' 2.7 +/- 5.4 1.2 +/- 3 0 66 12/31/01 03/25/02 07/01/02 09/30/02
- 03/25/02
- 07/01/02 09/30/02 12/30/02
< 0.2
< 0.7
< 5 2
< 6 6
< 0 2
< 0 2
< 1.4
< 4 4 C
12/31/01 03/25/02 07/01/02 09130/02
- 03/25/02
- 07/01/02
- 09/30/02
- 12/30/02
< 0 2
< 0 5
< 4.1
< 5.5
< 0.1
< 01
< 15
< 3.6 MEAN*
32 +/- 64 1.5 +/- 39 MEAN 2.6 +/- 5 3 4.7 +/- 13 9 71 12/31/01 03/25/02 07/01/02 09/30/02
- 03/25/02
- 07/01/02
- 09/30/02
- 12130102
< 0 3
< 0 4
< 4.3
< 5 8
< 0.2
< 01
< 15
< 3 0 MEAN*
2.7 +/- 5 5 12 +/- 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, 2002 RESULTS IN UNITS OF E-3 PCI/CU METER +/- 2 SIGMA STC COLLECTION Be-7 Mn-54 Co-58 Co-60 Cs-134 Cs-137 PERIOD 3
12/31 - 03/25/02 62 +/- 10
<0 2
<0 2
< 0 4
< 0 3
<0.1 03/25 - 07/01/02 69 +/- 5
< 0 3
<0.4
< 0 3
< 0 3
< 0 3 07/01 - 09/30/02 69 +/- 7
< 0 4
<0.5
< 0 4
< 0.4
<0 4 09/30 - 12/30/02 66 +/- 45
< 0 4
<0.5
< 0 5
< 0.3
<0 4 MEAN' 66 +/- 7 03 +/- 0.2 04 +/- 03 04 +/- 02 03 +/- 0.1 03+/- 0.3 20 12/31 - 04/01/02 76+/- 10
<02
<04
<0.3
<0.3
<05 04/01 - 07101/02 84 +/- 6
<03
<04
< 02
< 02
<03 07101 - 09/30/02 78 +/- 6
<03
< 0 4
< 0.3
< 0 3
< 0 3 09/30 - 12/30/02 78 +/- 51
< 09
< 1 2
< 1.2
< 07
< 08 MEAN' 79 +/- 7 04 +/- 06 0.6 08 05 +/- 09 04 +/-045 05 +/- 05 66 12/31 - 04/01/02 77 +/- 11
<03
<0 2
< 04
<04
< 0 2 04/01 - 07/01/02 73 +/- 5
< 0 4
<06
< 0 4
<0 4
< 0 4 07/01 - 09/30/02 82 +/- 8
< 0 4
<0.4
< 04
<0 3
<04 09/30 - 12/30/02 74 +/- 68
<1 0
<1.3
< 1 2
< 0 8
< 0.9 MEAN' 77+/- 8 05+/- 0.6 06+/- 1.0 06+/- 08 05+/- 05 05+/- 06 71 12/31 - 04/01/02 73 +/- 9
<0.3
<02
< 04
< 04
< 02 04/01 - 07/01102 72 +/- 5
<0.4
<0.5
< 0 3
< 0.4
< 04 07/01 - 09130/02 65 +/- 5
<0.3
< 04
< 04
< 0.2
< 0 2 09/30 - 12/30/02 73 +/- 53
<1 0
<1.1
< 08
< 0.7
< 08 MEAN*
71 +/- 8 0.5 +/- 06 06 +/-08 05 +/- 0.5 04 +/- 0.4 04 +/- 06 72 12/31 - 04/01/02 70 +/- 10
<02
<02
< 0.3
< 0.3
< 01 04101 - 07/01/02 67 +/- 4
<0 2
< 0 3
< 0 2
< 0 2
< 0.2 07101 - 09130/02 77 +/- 7
<0 3
< 0 3
< 0.3
< 0 2
<0 2 09/30 - 12130102 77+/- 52
<06
<11
<07
<06
<08 MEAN*
73 +/- 10 03 +/- 04 05 +/- 08 04 +/- 05 03 +/- 0.3 03 +/- 06 73 12/31 - 04/01102 65 +/- 10
<02
< 03
< 03
< 03
< 02 04/01 - 07/01/02 64 +/- 5
<03
<04
< 0.3
< 0.3
< 03 07/01 - 09130/02 60 +/- 5
<0 3
< 0.5
< 0 3
< 0 3
<0 3 09/30 - 12/30/02 62 +/- 41
<0 8
<0 9
< 0 8
< 0 6
<0 7 MEAN*
63+/- 5 04+/- 05 05+/-0 6 04+/- 05 04+/- 03 04 04 C
12/31 - 04/01102 64 +/- 11
< 02
< 02
< 0.3
<03
< 02 04/01 - 07101102 58 +/- 4
<03
<04
< 03
< 03
< 03 07/01 - 09/30/02 67 +/- 5
<0 3
<0 4
< 0 3
< 0 3
< 0 3 09/30 - 12130102 67 +/- 26
<03
< 04
< 05
< 02
< 03 MEAN' 64+/- 9 03+/- 01 04+/- 02 03+/- 02 03+/- 01 03+/- 0.1
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES C-i 3
TABLE C-VI.1 CONCENTRATIONS OF 1-131 IN AIR IODINE SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2002 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 MEAN 20
<5
< 5
< 3
<4
< 2
<5
< 4
< 3
< 7
< 3
< 2
< 3
< 4
< 2
< 6
< 12
< 9
< 8
< 6
< 8
< 9
< 6
< 10
<8
<8
< 8
< 16 7
<4
' 11
<7
< 7
< 7
< 13
<5
< 19
< 7
< 15
<19
<5
< 3
< 17
' 12
< 22
< 6
<5
< 4
< 3
< 3
<1
< 9
< 5 7 +/- 9 66
<6
<6
< 5
<4
< 2
<6
< 5
< 3
< 8
< 3
< 3
< 4
< 6
<3
<7
< 13
< 9
< 8
< 7
<9
<6
< 6
< 10
< 9
< 8
< 9
< 18
<8
<5
< 12
< 8
< 8
< 12
<9
<6
< 21
< 8
< 17
< 21
< 6
<4
- 19
< 14
< 25
< 7
<6
< 5
< 5
< 3
< 1
< 10
<6 71
<6
<7
<4
<3
<3
<5
<5
<5 5
3
<2
<3
<7
<3
< 6
<12
< 9
<7 4
6
<5
<7
<8
<5 4
7
< 18
< 9
<4
< 9 5
5
<9 8
6
< 18
<7
< 9
<24
<7
<3
< 9
- 14
<69
<3
<2
< 3
<4
<3
<1
<5
<5 GROUP II 72
<7
< 6
< 4
< 3
< 3
< 5
< 5
<5
< 5
< 3
< 2
<3
<5
<4
< 6
< 12
<9
< 7
<5 6
<9
< 119
< 10
< 8
<7
< 8
< 21
<9
< 5
<9
<5
< 5
- 10
- 12
< 5
< 18
<7
<9
< 24
< 7
< 5
- 13
< 14
- 10
<3
< 12
< 3
<4
< 6
< 3
<5
<5
(,
73
<5
< 7
< 4
< 3
< 3
<4
<5
<5
<5
<3
<2
< 3
< 4
< 3
<6
< 11
<8
< 6
< 4
< 6
<5
- 1)
<6
<8
<7
< 6
<3
< 16
<8
< 4
<9
< 5
<5
<8
< 11
< 5
<17
<7
<9
< 23
<6
<5
< 13
< 13
- 10
< 3
<8
<3
<2
<5
< 4
<8
<6 C
< 6
<4
< 3
<4
<2
< 6
< 3
< 3
<6
< 2
<2
< 3
< 4
< 3
<6
< 12
< 6
<8
<5
<7
<5
< 5
< 9
< 7
<7
< 2
< 15
< 7
< 5
< 9
< 7
< 6
< 9
< 12
< 3
< 17
< 6
< 14
< 18
< 5
<3
< 16
< 11
< 20
<6
< 5
<4
< 3
<4
< 8
< 5 GROUP III 3
< 6
<4
<3
<4
< 2
< 6
<4
<3
< 7
<3
<2 3
<3
< 3
<6
< 15
< 7 9
<5
<8
<9
< 6
< 10
< 8
<8
< 4
< 16
<7
< 5
< 10
< 11
<7
< 9
< 8
<7
< 19
<7
< 15
< 19
< 5
< 6
< 17
- 12
- 22
< 6
< 5
<4
<3
<4
'<1
< 9
< 5 8 +/- 10 8 +/- 19 10 +/- 32 7 +/-8 7 +/- 9 7 +/- 10 (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, 2002 RESULTS IN UNITS OF PCI/KG WET +/- 2 SIGMA Sr-89 Sr-90 K-40 1-131 Cs-134 Cs-137 Ba-140 I
cnf STC COLLECTION PERIOD 35 08/07/02 Cabbage 35 08/07/02 Collards 35 09/10/02 Broadleaf 35 10/10/02 Broadleaf MEAN*
U La-140
< 24
< 38
< 28
< 12 26 +/- 22 4 +/-2 8 +/-3 84 +/- 5 36 +/- 3 41 +/- 81 2710 +/- 204 4030 +/- 325 2220 +/- 514 1640 +/- 368 2650 +/- 2037
< 62
< 102
< 1150
< 554 467 +/- 1014
< 18
< 31
< 49
< 34 33 i 25 28 +/- 6
< 36
< 47
< 37 37 +/- 16
< 127
< 197
< 1040
< 675 510 t 859
< 40
< 13
< 344
< 217 154 +/- 312
' THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES
TABLE C-VI1.1 CONCENTRATIONS OF STRONTIUM AND GAMMA EMITTERS IN VEGETATION SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2002 RESULTS IN UNITS OF PCI/KG WET +/- 2 SIGMA STC COLLECTION PERIOD 36 08/06102 Cabbage 36 08/06/02 Collards 36 09/10/02 Cabbage 36 09/10/02 Mustard Greens 36 09/10/02 Collards 36 10/10/02 Cabbage 36 10/10/02 Collards Sr-89
< 10
< 14
< 8
< 25
< 23
< 7
< 11 Sr-90 6 +/- 1 12 +/- 1 3 +/-1 5 +/-2 9 +/-3 4 +/-1 9 +/-2 K-40 1-131 Cs-134 Cs-137 Ba-140 2880 +/- 153 3820 +/- 211 3000 +/- 427 6860 +/- 279 6080 +/- 372 2790 +/- 139 4950 +/- 221
< 23
< 50
< 400
< 164
< 326
< 96
< 115 La-140
< 5
< 15
< 22
< 7
< 13
< 5
< 7
< 6
< 13
< 23
< 8
< 15
< 5
< 7
< 45
< 103
< 485
< 173
< 353
< 106
< 136
< 15
< 31
< 149
< 53
< 106
< 33
< 44 C-C, MEAN*
14 +/- 14 7 +/- 6 4340 i 3302 168 +/- 285 11 +/- 13 11 +/- 13 200 +/- 318 62 +/- 96
- 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, 2002 RESULTS IN UNITS OF PCI/KG WET +/- 2 SIGMA STC COLLECTION Sr-89 Sr-90 K-40 1-131 Cs-134 Cs-137 Ba-140 La-140 PERIOD 66 08/07102
<30
< 5 3000 +/- 175
<28
< 7 15 +/- 4
< 60
< 18 Cabbage 66 08/07/02
<11 4
1 3060 +/- 338
< 91
< 27
< 27
< 187
< 57 Collards 66 09/10/02
< 23 121 8
2090 +/- 284
< 483
< 23
< 26
< 520
< 164 Broadleaf 66 09/10/02
< 11 3
1 2770 +/- 298
< 147
< 7
< 9
< 172
< 54 Cabbage 66 10/10/02
< 3 29 1
3720 +/- 458
< 602
< 36
< 41
< 690
< 228 Broadleaf MEAN' 16 +/- 21 32 102 2928 +/- 1173 270 +/- 511 20 +/- 25 23 +/- 25 326 +/- 533 104 +/- 176
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES I,
TABLE C-VIlI.1 QUARTERLY TLD RESULTS FOR OYSTER CREEK GENERATION STATION, 2002 RESULTS IN UNITS OF MILLI-ROENTGEN/STD. QUARTER +/- 2 STANDARD DEVIATIONS STATION MEAN JAN - MAR APR - JUN JUL - SEP OCT - DEC CODE i2S. D.
C 11.9 +/- 1.8 114 2.3 110 2.3 130 2.4 12.4 1.1 14 135+/- 26 128 0.9 120 1.6 148i 1.9 143 1.7 1
134+/- 3.8 151+/- 1.2 108+/- 1.1 146+/- 1.2 130+/- 1.9 TI 139 +/- 4.1 151 +/- 1.2 108 1.1 145 1.1 15.1 +/- 93 3
10.7 +/- 4.1 120 +/- 64 78 i 09 123 i 1.4 106 +/- 13 6
11.9 +/- 7.2 16.4 +/- 19.1 7.7 i 0.0 126 1.8 10.8 i 07 8
11.1 +/- 4.9 12 6 +/- 0 9 7.7 +/- 0 0 13.1 i 1.1 11.0 +/- 2.0 9
11.9 +/- 52 136 +/-09 8.1 +/- 2.2 135 +/- 1.1 12.2 +/- 1.5 11 11.1 +/- 45 12.4 +/- 1.1 7.9 +/- 1.6 12.9 +/- 1.7 11.0 +/- 1.2 22 104 +/- 5.5 11.8 +/- 1.2 6.7 +/- 1.3 13.0 +/- 1.1 101 +/- 1.5 51 14.0 3 8 16 2 19 116 +/- 1.7 14.3 +/- 1.0 14.1 +/- 3 6 52 15.7 31 17.4 1.1 137 +/- 1.6 162 +/- 1.5 156 +/- 1.0 53 15.4 +/- 4.1 17.6 +/- 1.7 137 +/- 1.6 167 +/- 1.4 13.6 +/- 1.4 54 11.7 37 136 +/-09 9.7 +/- 2.2 12.8 +/- 0.8 106 +/- 07 55 199 +/- 26 21.6 1.2 184 +/- 2 5 199 +/- 2.1 198 +/- 2.0 56 180 +/- 2.0 18.9 +/- 2.0 166 +/- 2.6 18.3 +/- 1.4 184 +/- 46 57 14.9 +/- 2.7 16 5 +/- 1.7 13.7 i 2.1 15 6 +/- 1.9 13 9 +/- 2.9 58 15 7 +/- 32 17.4 23 15.1 +/- 15.1 16.4 +/- 1.9 13 8 +/- 1.5 59 14.1 +/- 4.7 146 i 00 11.2 +/- 1.9 13.8 +/- 2.2 16.9 +/- 109 61 12.2 +/- 3 1 13.1 +/- 1.1 10 0 +/- 1.9 12.1 +/- 1.0 13.4 +/- 1.2 62 13.2 +/- 1.2 13.5 i 1.4 (1) 12.5 +/- 0.9 13.6 +/- 1.9 63 12.4+/- 37 12.6+/- 09 100+/- 1.9 12.6+/- 1.7 145+/- 08 64 12.6 +/- 28 12.9 +/- 1 2 106 +/- 1.2 12.8 +/- 1.0 139 +/- 1.6 65 12.3 +/- 3 0 13 3 +/- 0.9 10 2 +/- 2.1 124 +/- 1.7 13 4 +/- 1.3 66 108 +/- 2.6 102 +/- 1.9 9.3 +/- 1.1 12.2 +/- 24 11.4+/- 2.7 68 12.0 +/- 4.4 11.4 +/- 09 93 +/- 1.2 12.7 +/- 08 14.5 +/- 1.2 71 12.2 +/- 2.9 11.1 +/- 1.1 10.8 +/- 1.1 13.2 +/- 1.8 13.6 +/- 1.3 72 11.3 +/- 29 9.9 +/- 1.1 103 +/- 2.5 130 +/- 1.6 12.1 +/- 1.9 73 109 +/- 39 9.5 +/- 1.7 89 +/- 1.3 12.2 +/- 1.5 12.9 +/- 30 74 11.2 +/- 3.0 11.0 +/- 09 9.1 +/- 1.3 123 +/- 0.8 122 +/- 2.4 75 12.5 +/- 3 5 13.1 +/- 1.8 9.9 +/- 1.7 13 3 +/- 1.3 13.6 +/- 0.9 78 11.1 +/- 4.4 11.7 +/- 1.1 7.9 +/- 09 11.8 +/- 1 8 12.9 +/- 33 79 11.2 +/- 3.0 11.4 +/-0.9 92 +/- 32 11.3 +/- 0.4 128 +/- 1.0 81 109 +/- 3.8 12.0 +/- 1.1 8.1 +/- 1.1 11.6 +/- 1.0 12.0 +/- 2.0 82 11.6 +/- 32 12.4 +/- 1.4 9.3 +/- 2.1 120 +/- 1.5 12.9 +/- 20 84 11.6 +/- 34 13.3 +/- 1.7 9.7 +/- 2.1 10.7 +/- 1.6 12 8 +/- 2.7 85 10.9 i 32 11.2 +/- 0.0 86 +/- 1.6 12.2 +/- 1.7 11.7 +/- 42 86 102 +/- 48 (1) 100 +/- 1.3 12.7 +/- 1.3 7.9 +/- 07 88 100 +/- 5.3 9.4 +/- 1.7 67 +/- 00 11.1 +/- 1.1 130 +/- 1.9 89 10.1 +/- 35 9.2 +/- 1.2 8.3 +/- 15.8 12.3 +/- 2.2 107 +/- 08 90 10.1 +/- 2.9 9.2 +/- 1 2 8.7 +/- 1.9 119 +/- 08 10.7 +/- 2.0 92 11.6 +/- 3.5 11.2 +/- 1.2 93 +/- 2.2 127 +/- 1.4 132 +/- 1.4 98 13 0 +/- 48 13.1 +/- 1.1 10 0 +/- 1.6 15.9 +/- 12 2 13 1 +/- 08 99 11.3 +/- 3.4 125 +/- 0.9 88 +/- 1.3 12.2 +/- 1.6 11.5 +/- 1.7 (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-1 8
TABLE C-VIII.2 MEAN QUARTERLY TLD RESULTS FOR THE SITE BOUNDARY, MIDDLE, SPECIAL INTEREST AND CONTROL LOCATIONS FOR OYSTER CREEK GENERATING STATION, 2002 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 15 3 +/- 5.7 12.3 +/- 5.5 14.6 +/- 4.8 14.4 +/- 4.7 12.2 +/- 3 0 88 +/- 1.9 12.5 +/-2.3 120 +/-3.1 11.3 +/- 4.0 8.9 +/- 2.8 12.7 +/- 1.9 12.2 +/- 3.0 12.1 +/- 2.0 11.5 +/- 1.4 13 9 +/- 2.5 13.4 +/- 27 TABLE C-VIII.3
SUMMARY
OF THE AMBIENT DOSIMETRY PROGRAM FOR OYSTER CREEK GENERATING STATION, 2002 RESULTS IN UNITS OF MILLI-ROENTGEN/STD. QUARTER LOCATION SAMPLES ANALYZED PERIOD PERIOD MINIMUM MAXIMUM SITE BOUNDARY MIDDLE DISTANCE SPECIAL INTEREST CONTROL Da 63 40 8
6.7 6.7 6.7 11 0 Z1.0 16.4 15.1 14.8 PERIOD MEAN
+/- 2 s.d.
14.2 +/- 5.5 11.4 +/- 4.0 11.3 +/- 4.2 12.7 +/- 2.6 SITE BOUNDARY STATIONS - 1, 51, 52, 53,54,55,56, 57, 58, 59,61,62, 63, 64,65,66 MIDDLE DISTANCE STATIONS - 6, 8, 22, 68, 73,74,75, 78,79,81, 82,84,85, 86,98,99 SPECIAL INTEREST - 3, 9,11, 71. 72, 88, 89, 90, 92, Ti CONTROL STATIONS - C, 14 C-1 9
TABLE C-IX.1
SUMMARY
OF COLLECTION DATES FOR SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2002 SURFACE WATER (TRITIUM LIQUID SCINTILLATION)
COLLECTION PERIOD JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC 04 23 24 33 94 01102102 01/02/02 02/13/02 02113/02 03112102 03112102 4/09/02 04/09102 04109/02 04109/02 03105/02 03/05/02 06/04102 06/04102 07/05102 07/05/02 08/02/02 08/02102 9/04/02 09/04102 09/04/02 09104102 10/02102 10102/02 11105/02 11105/02 12/03102 12103102 SURFACE WATER (GAMMA SPECTROSCOPY)
COLLECTION PERIOD JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC 23 24 33 94 01/02102 01/02/02 02113/02 02113/02 03/12102 03/12102 1109102 04/09/02 04109/02 04109/02 03105102 03105/02 06104/02 06/04/02 07105/02 07/05/02 08/02/02 08/02/02 9/04/02 09104/02 09/04/02 09104102 10/02/02 10/02/02 11/05/02 11/05/02 12103/02 12/03/02 WELL WATER (TRITIUM & GAMMA SPECTROSCOPY)
COLLECTION PERIOD JAN-MAR APR-JUN JUL-SEP OCT-DEC 37 38 02/19/02 02/15/02 02/15/02 03/27/02 - 05/10102 03127/02 - 05/10/02 03/27/02 - 05110102 06/06/02 - 08112/02 06106/02 - 08/12/02 06106/02 - 08/12/02 09106/02 - 11/07/02 09/06102 - 11/07/02 09/06102 - 11107102 AIR PARTICULATE (GAMMA SPECTROSCOPY)
COLLECTION PERIOD C
3 20 66 JAN-MAR APR-JUN JUL-SEP OCT-DEC COLLECTION PERIOD JAN-MAR APR-JUN JUL-SEP OCT-DEC 12131/01 - 04/01102 12131/01 -
04/01102 12131/01 - 04101/02 12/31101 - 04101/02 03125/02 - 07/01/02 04101/02 -
07/01/02 04101/02 - 07101/02 04/01/02 - 07/01/02 07/01102 - 09/30102 07/01102 -
09130/02 07101102 - 09130/02 07101/02 - 09130102 09130102 - 12/30/02 09130/02 -
12130102 09130102 - 12/30102 09130/02 - 12130102 71 72 73 12131/01 - 04101102 12131101 - 04/01102 12131/01 -
04101102 04101102 - 07/01102 03125/02 - 07/01/02 04101102 -
07/01102 07101/02 - 09130102 07101/02 - 09130/02 07101/02 -
09130/02 09130/02 - 12t30102 09130/02 - 12/30/02 09130/02 -
12t30/02 C-20
TABLE C-IX.1
SUMMARY
OF COLLECTION DATES FOR SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2002 AIR PARTICULATE (GROSS BETA & 1-131)
COLLECTION C
3 20 66 PERIOD 71 71 I
1/fiJl/U
- U'iUbU'4 2
01/08/02 - 01/14/02 3
01/14/02 - 01/22102 4
01/22102 - 01/29/02 5
01/29/02 - 02104102 6
02/04/02 - 02/11/02 7
02J11/02 - 02118/02 8
02/18/02 - 02/25/02 9
02/25/02 - 03/04/02 10 03/04102 - 03/11/02 11 03/11102 - 03/19/02 12 03/19/02 - 03/25102 13 03/26/02 - 04/02102 14 04/02/02 - 04108/02 15 04/08/02 - 04/16/02 16 04/16/02 - 04/23102 17 04/23102 - 04/29/02 18 04/29102 - 05/07102 19 05/07/02 - 05/13/02 20 05113102 - 05/20102 21 05/20/02 - 05/28102 22 05/28/02 - 06/04102 23 06/04/02 - 06/10/02 24 06/10/02 - 06/17/02 25 06/17/02 - 06/24/02 26 06/24/02 - 07101/02 27 07/01/02 - 07/08/02 28 07/08/02 - 07/15/02 29 07/15/02 - 07/22102 30 07/22/02 - 07/29102 31 07/29/02 - 08/05/02 32 08/05/02 - 08/13/02 33 08113/02 - 08/19102 34 08119/02 - 08/26/02 35 08/26/02 - 09/03/02 36 09/03/02 - 09/09/02 37 09/09102 - 09/17/02 38 09/17102 - 09/24/02 39 09124102 - 09/30/02 40 09/30/02 - 10107/02 41 10/07/02 - 10/14/02 42 10/14/02 - 10/21/02 43 10/21/02 - 10/28/02 44 10/28102 - 11/04/02 45 11/04/02 - 11/11/02 46 11/11102 - 11/18/02 47 11/18/02 - 11/25/02 48 11125/02 - 12102102 49 12/02102 - 12/09102 50 12J09/02 - 12116/02 51 12116/02 - 12/23/02 52 12123/02 - 12/30102
...... I--
1 PS4141\\1 Ia/rl71n_
IaytJI3ul
- U IU/iUz 01/07102 - 01/14/02 01/14/02 - 01/21/02 01/21/02 - 01/28/02 01/28/02 - 02/04102 02104/02 - 02111/02 02t11/02 - 02118/02 02/18102 - 02/25/02 02/25/02 - 03/04/02 03/04/02 - 03/11/02 03/11/02 - 03/18/02 03/18/02 - 03/25/02 03125102 - 04/01/02 04/01/02 - 04/08102 04/08102 - 04/15/02 04115/02 - 04122102 04/22102 - 04/29102 04129102 - 05/06/02 05/06/02 - 05113102 05113/02 - 05120/02 05/20/02 - 05/27/02 05/27/02 - 06/03/02 06/03/02 - 06/10/02 06/10/02 - 06117/02 06/17/02 - 06/24102 06/24/02 - 07/01/02 07/01102 - 07/08/02 07/08102 - 07/15/02 07/15102 - 07122102 07/22102 - 07129102 07129/02 - 08105102 08105102 - 08/12102 08/12102 - 08/19/02 08119/02 - 08/26102 08/26102 - 09/02102 09/02t02 - 09/09/02 09/09/02 - 09/16/02 09/16/02 - 09/23/02 09/23/02 - 09/30/02 09/30/02 - 10/07/02 10/07/02 - 10/14/02 10/14/02 - 10121/02 10/21/02 - 10/28/02 10/28/02 - 11/04/02 11/04/02 - 11/11/02 11/111/02 - 11/18/02 11/18/02 - 11/25/02 11/25/02 - 12/02102 12102102 - 12109/02 12109/02 - 12116/02 12116102 - 12/23/02 12123t02 - 12/30/02 Idi3i11U
- UllU(/Uz 01/07/02 - 01/14/02 01/14/02 - 01/21/02 01/21/02 - 01/28/02 01/28102 - 02104/02 02/04/02 - 02t11/02 02/111/02 - 02/18/02 02118/02 - 02125/02 02125/02 - 03104/02 03/04/02 - 03/11/02 03/11/02 - 03/18/02 03/18/02 - 03/25/02 03125/02 - 04/01/02 04/01/02 - 04/08/02 04/08/02 - 04/15/02 04/15102 - 04/22/02 04/22t02 - 04/29/02 04/29/02 - 05106102 05/06102 - 05/13/02 05/13/02 - 05/20/02 05/20102 - 05/27/02 05/27/02 - 06103/02 06/03/02 - 06/10/02 06/10/02 - 06/17/02 06/17/02 - 06/24/02 06124/02 - 07/01/02 07/01/02 - 07108/02 07/08/02 - 07115102 07/15/02 - 07/22/02 07/22/02 - 07/29102 07/29/02 - 08/05/02 08/05102 - 08/12102 08/12102 - 08/19/02 08/19/02 - 08/26102 08126/02 - 09/02/02 09/02/02 - 09/09/02 09/09/02 - 09/16/02 09/16102 - 09123/02 09/23/02 - 09/30102 09/30/02 - 10/07/02 10/07/02 - 10/14/02 10/14/02 - 10/21102 10/21/02 - 10/28/02 10/28102 - 11/04/02 11/04/02 - 11/11102 11/11/02 - 11/18/02 11/18102 - 11/25/02 11/25102 - 12102102 12102102 - 12109102 12109/02 - 12116/02 12116/02 - 12/23/02 12/23/02 - 12130/02 fLiallUl - UIUiilUz 01/07102 - 01/14/02 01/14/02 - 01/21/02 01/21102 - 01/28/02 01128102 - 02104/02 02/04102 - 02111/02 02/11/02 - 02118/02 02/18102 - 02t25/02 02/25102 - 03104/02 03/04/02 - 03111/02 03/11/02 - 03118/02 03/18/02 - 03/25/02 03125/02 -
4/01/02 04/01/02 - 04/08/02 04/08102 - 04/15/02 04/15102 - 04/22/02 04/22102 - 04/29/02 04/29102 - 05106/02 05/06/02 - 05113/02 05/13t02 - 05t20/02 05/20/02 - 05127/02 05/27/02 - 06/03/02 06/03/02 - 06/10/02 06/10102 - 06/17/02 06/17/02 - 06/24/02 06/24102 - 07/01/02 07/01/02 - 07/081/02 07/08102 - 07115/02 07/15102 - 07/22/02 07/22102 - 07/29/02 07/29102 - 08105/02 08105t02 - 08112102 08/12102 - 08/19/02 08/19/02 - 08126/02 08/26102 - 09/02102 09/0202 - 09109/02 09/09/02 - 09116/02 09/16/02 - 09/23/02 09/23102 - 09/30/02 09/30/02 - 10/07/02 10/07/02 - 10/14/02 10/14/02 - 10/21/02 10/21/02 - 10128/02 10/28102 - 11/04102 11104/02 - 11/11/02 11/11/02 - 11/18/02 11/18102 - 11/25/02 11/25102 - 12102/02 12102/02 - 12t09/02 12V09/02 - 12116/02 12116102 - 1223/02 12/23/02 - 12130/02 1IJ
--U107UT 01/07102 - 01/14/02 01/14102 - 01121/02 01/21102 - 01/28/02 01/28/02 - 0204/02 02t04/02 - 02111/02 0211102 - 02/18/02 02118102 - 02125/02 0225102 - 03/04/02 03/04102 - 03/11/02 03/11102 - 03/18/02 03/18/02 - 03/25/02 03/25102 - 04/01/02 04/01/02 - 04/08/02 04/08/02 - 04/15/02 04/15/02 - 04/22102 04/22102 - 04/29/02 04/29/02 - 05106/02 05/06102 - 05/13/02 05/13102 - 05/20/02 05/20102 - 05/27/02 05127/02 - 06103/02 06/03102 - 06110/02 06/10/02 - 06/17/02 06/17/02 - 06/24102 06/24/02 - 07/01102 07/01/02 - 07108/02 07108102 - 07/15/02 07/15102 - 07/22102 07/22102 - 07/29/02 07/29/02 - 08/05/02 08/05/02 - 08/12102 08/12102 - 08/19/02 08/19102 - 08/26/02 08/26/02 - 0902102 09/02t02 - 09/09102 09/09/02 - 09116/02 09/16/02 - 09/23102 09123/02 - 09/30/02 09/30/02 - 10/07/02 10/07/02 - 10/14/02 10/14/02 - 10/21/02 10/21/02 - 10/28/02 10/28/02 - 11/04/02 11/04/02 - 11/11/02 1111/02 - 11/18/02 11/18/02 - 11/25/02 11/25/02 -
12102102 12102102 - 1209/02 12109/02 - 12t16t02 12/16/02 - 12/23/02 12/23/02 - 12/30102 C-21
I TABLE C-IX.1
SUMMARY
OF COLLECTION DATES FOR SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2002 AIR PARTICULATE (GROSS BETA & 1-131)
COLLECTION PERIOD l-u-'-
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 12/31/U1 -
U11Ud/UZ 01/08/02 - 01/14102 01114/02 - 01/22102 01/22/02 - 01/29/02 01129/02 - 02104/02 02/04/02 - 02111/02 02111/02 - 02118102 02118102 - 02/25/02 02/25102 - 03/04/02 03/04/02 - 03/11/02 03/11/02 - 03119/02 03119102 - 03/25/02 03/26102 - 04102/02 04/02/02 - 04/08/02 04/08/02 - 04/16/02 04/16/02 - 04/23/02 04/23/02 - 04/29102 04129/02 - 05/07102 05107/02 - 05/13102 05/13/02 - 05/20/02 05/20102 - 05/28/02 05/28/02 - 06/04/02 06/04102 - 06110102 06/10102 - 06117102 06/17102 - 06/24/02 06/24102 - 07/01102 07/01/02 - 07/08/02 07/08/02 - 07/15102 07115102 - 07/22/02 07/22/02 - 07/29102 07129/02 - 08/05/02 08105/02 - 08/13/02 08/13102 - 08/19/02 08119102 - 08/26/02 08126102 - 09103/02 09/03/02 - 09/09/02 09109/02 - 09/17/02 09117/02 - 09/24/02 09/24/02 - 09/30/02 09130/02 - 10/07/02 10/07/02 - 10/14/02 10/14/02 - 10/21102 10/21102 - 10/28/02 10/28102 - 11/04/02 11/04102 -
11/11/02 1111/02 -
11/18/02 11/18/02 - 11/25102 11/25/02 -
12/02102 12/02102 - 12/09/02 12/09102 - 12/16/02 12/16/02 - 12/23/02 12123102 -12/30102 UT - UlUlluL 01107/02 - 01114/02 01/14102 - 01/21/02 01/21/02 - 01/28/02 01/28102 - 02/04102 02/04/02 - 02/111/02 02111/02 - 02/18/02 02118102 - 02/25/02 02/25/02 - 03104/02 03/04/02 - 03/11/02 03/11/02 - 03/18/02 03/18/02 - 03/25/02 03125102 - 04101/02 04/01102 - 04/08/02 04108/02 - 04115102 04/15/02 - 04/22/02 04122/02 - 04/29102 04/29/02 - 05/06102 05/06102 - 05/13/02 05/13/02 - 05120/02 05120102 - 05/27/02 05/27102 - 06/03102 06/03102 - 06/10/02 06110102 - 06117102 06/17/02 - 06/24/02 06/24/02 - 07/01102 07/01/02 - 07/08/02 07108102 - 07/15/02 07/15102 -07/22/02 07/22/02 - 07/29/02 07/29/02 - 08105/02 08105/02 - 08/12/02 08/12/02 - 08/19/02 08/19102 - 08/26/02 08/26102 - 09/02102 09/02/02 - 09/09/02 09/09102 - 09/16/02 09116/02 - 09/23102 09123/02 - 09/30/02 09/30102 - 10107102 10/07/02 - 10/14/02 10114/02 - 10121/02 10121102 - 10/28/02 10/28102 - 11104102 11/04102 - 11/11/02 11111/02 - -11/18/02 11/18/02 - 11 25102 11/25/02 - 12/02/02 12/02/02 - 12/09/02 12/09/02 - 12/16/02 12/16/02 - 12/23/02 12/23102 - 12130/02 C-22
TABLE C-IX.1
SUMMARY
OF COLLECTION DATES FOR SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2002 TLD STATION CODE C
14 1
Ti 3
6 a
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 01114/02 - 04/15/02 01/14102 - 04/15102 01/14/02 - 04/15102 01/14/02 - 04/15/02 01/14102 - 04/15/02 01/14/02 -04/15/02 01/14/02 - 04/15/02 01/14/02 - 04115102 01114/02 - 04/15/02 01/14/02 - 04/15102 01/14/02 - 04/15102 01/14/02 - 04/15102 01/14102 - 04/15102 01/14102 - 04/15102 01/14/02 - 04115102 01/14/02 - 04/15102 01/14/02 - 04/15102 01114102 - 04/15102 01/14/02 - 04/15102 01/14102 - 04/15/02 01/14/02 - 04/15102 01/14/02 - 04/15102 01/14/02 - 04/15102 01/14/02 - 04/15102 01/14/02 - 04/15102 01/14102 - 04/15102 01/14/02 - 04/15102 01/14/02 - 04/15102 01/14/02 - 04/15/02 01/14/02 - 04115102 01/14/02 - 04/15102 01/14102 - 04/15102 01/14102 - 04/15/02 01/14/02 - 04/15/02 01114/02 - 04/15102 01/14/02 - 04/15102 01/14/02 - 04/15/02 01/14102 - 04/15/02 01/14102 - 04115102 01/14/02 - 04/15102 01/14/02 - 04/15102 01/14/02 - 04/15102 01/14/02 - 04115/02 01114/02 - 04/15/02 04/15/02 - 07/15/02 04/15/02 - 07115102 04/15102 - 07/15/02 04/15102 - 07/15/02 04115102 - 07/15/02 04115102 - 07/15102 04/15/02 - 07/15/02 04/15102 - 07/15/02 04/15102 - 07115/02 04/15/02 - 07115/02 04/15102 - 07/15/02 04/15/02 - 07/15/02 04/15/02 - 07/15/02 04/15102 - 07/15/02 04/15/02 - 07/15102 04/15/02 - 07115/02 04/15/02 - 07115/02 04/15102 - 07/15/02 04/15102 -07115102 04/15102 - 07/15/02 04/15102 - 07115102 04/15/02 - 07/15/02 04/15/02 - 07/15102 04/15/02 - 07/15/02 04/15/02 - 07/15/02 04/15102 - 07/15/02 04/15102 - 07/15/02 04115102 - 07115/02 04/15/02 - 07/15102 04/15/02 - 07/15/02 04/15/02 - 07/15/02 04/15/02 - 07115102 04/15102 - 07/15/02 04/15/02 - 07/15/02 04/15/02 - 07/15102 04/15/02 -07/15/02 04/15/02 - 07/15/02 04115/02 - 07/15/02 04115102 - 07/15/02 04/15102 - 07/15/02 04/15102 - 07)15/02 04/15/02 - 07/15102 04/15/02 - 07/15/02 04/15102 - 07115102 07/15102 - 10/14/02 07/15/02 - 10/14/02 07/15/02 - 10114/02 07/15/02 - 1014/02 07/15102 - 10114102 07/15102 - 10/14102 07/15/02 - 10/14102 07/15/02 - 10/14/02 07/15/02 - 10114/02 07/15/02 - 10/14/02 07115/02 - 10114/02 07/15/02 - 10/14/02 07/15/02 - 10/14/02 07/15102 - 10/14/02 07/15102 - 10/14/02 07/15102 - 10/14/02 07115/02 -
10114/02 07/15102 - 10/14/02 07/15/02 - 10/14/02 07115102 - 10/14102 07/15102 - 10/14/02 07/15/02 - 10/14/02 07/15102 - 10/14102 07/15/02 - 10114/02 07/15/02 - 10/14/02 07/15102 - 10/14/02 07/15/02 - 10114/02 07/15102 - 10/14/02 07115/02 - 10/14/02 07/15102 - 10/14/02 07/15/02 - 10/14102 07115/02 - 10114102 07115/02 - 10/14/02 07/15/02 - 10/14/02 07/15102 - 10/14/02 07/15/02 - 10/14/02 07/15/02 - 10/14/02 07/15102 - 10114/02 07/15/02 - 10/14/02 07/15/02 - 10/14/02 07115/02 - 10/14/02 07115102 - 10/14/02 07115/02 - 10/14/02 07/15/02 - 10114102 10/14/02 - 01113103 10114/02 - 01/13/03 10114102 - 01/13103 10/14/02 - 01/13/03 10/14/02 - 01/13103 10/14/02 - 01/13/03 10/14/02 - 01/13/03 10/14/02 - 01113103 10/14/02 - 01/13/03 10114102 - 01/13103 10114102 - 01/13103 10/14/02 - 01/13103 10/14/02 - 01/13103 10/14102 - 01/13/03 10/14/02 - 01/13/03 10/14/02 - 01/13/03 10114/02 - 01/13/03 10/14/02 - 01/13/03 10/14/02 - 01/13/03 10/14/02 - 01/13103 10/14/02 - 01/13/03 10/14/02 - 01113103 10/14102 - 01/13103 10/14102 - 01/13103 10/14/02 - 01/13103 10114/02 - 01/13/03 10114/02 - 01/13103 10114/02 - 01113/03 10/14/02 - 01/13/03 10/14/02 - 01/13/03 10/14/02 - 01/13/03 10/14/02 - 01/13/03 10/14/02 - 01/13/03 10/14/02 - 01/13/03 10/14/02 - 01/13/03 10/14/02 - 01/13/03 10/14/02 - 01/13/03 10/14/02 - 01/13/03 10/14/02 - 01/13/03 10/14/02 - 01/13/03 10/14/02 - 01/13/03 10/14/02 - 01/13/03 10114102 - 01/13/03 10/14/02 - 01/13/03 C-23
FIGURE C-1 MEAN COBALT-60 CONCENTRATION IN CLAMS OYSTER CREEK GENERATING STATION, 1983 - 2002 20 INDICATORSTATION
--- BACKGROUND STATION
%5 0
5.
0 r
Ii m UN"
_ _1044 Hif t i ii m-muW P1U1-14 A1 _o pPl PM_
I tn ND 000 w X-X 4
m O
O m
v r
In N
> m 0 0 0 0 0 0 0 0 0 0000 000 0% 0f m
m 0
0%
0% 0%
0%
O CN 0%
0 O
0%
m 0m 0%0%
%0%0%%
%0 m
m
%0 0% 0 00 0% 0% 00 CA m
m 0%
-o --q "q ?-
?-q
?- T-.-I ?-
-q
?- ?- ?-
-o P-
?- ?- ? ?- r-
?-"
?- ?- ?-
YEAR
FIGURE C-2 MEAN COBALT-60 CONCENTRATION IN AQUATIC SEDIMENT OYSTER CREEK GENERATING STATION, 1984 - 2002 350 300 t INDICATOR STATION MEAN
-S BACKGROUND STATION MEAN 04 Po C)
Q 0
.w 250 200 150 100 50 0
tr r
tn 1
tn tn Io z
t-r-
o x
x cN 0e c
o4 m
qT tI
-b cO v-0 0 0 0000 0 0 0
X X
X X
X X
X00 000 00 XC 0
0% 0%
0%
0%
O O
0%
~C C\\
o\\
C\\
C\\
C\\
o>
0h C\\
Co 0%
Co oN 0
0%
C%
CO ON C\\
C\\
CN 0\\
C\\
o>
O
-4 V--
e4 YEAR
FIGURE C-3 MEAN CESIUM-137 CONCENTRATION IN AQUATIC SEDIMENT OYSTER CREEK GENERATING STATION, 1984 - 2002
-$- INDICATOR (Stations 23 & 24)
}
BACKGROUND (Station 94) 600 o400 I-t,PC Q
U Cl SW v
200 04 t
I t Itl m
fl Vn 0
%o
%0 t b t
w 0
X 00 0
0 i 0 0l N
M It It
%Z t'-
0W P-0000000 0000 00 00 00 000 00 00 00 000 0
'0w m
0NCN0 0% 0%
% % 0 0%ONc 0
C%
c r 0%
0%
0%
0%
m ak 0%
0%
0%
0 0
oe om m
m o
om om m
cm m
m 0%
0%
0
-9 4 r-
"4 r
N YEAR
FIGURE C-4 MEAN WEEKLY GROSS BETA CONCENTRATIONS IN AIR PARTICULATES OYSTER CREEK GENERATING STATION, 2002 4.OOE-02 Q 3.OOE-02 s
.0 c) 1.OOE-02 O.00E+O0 0
CI 0
0 I
I g
0 0
0 0
o 0
0 0
0 0
r4 0
"0 0
0 r~
0
~
e r
Date
FIGURE C-5 MEAN MONTHLY GROSS BETA CONCENTRATIONS IN AIR PARTICULATES OYSTER CREEK GENERATING STATION, 1984 - 2002 0.18 ICHERNOBYL ACCIDENT 0.16 4. -
..W.
. INDICATORSTATIONS BACKGROUND STATION
- c
.C
.C V
ea I*
Q 0
Ca 0.14 0.12 0.10 0.08.
0.06 -
0.04 -
0.02 0.00 l
l I..........l..
.I........... ll
§ll
. 1 I l
..l 1iI 1.
0 0 0 00 W
0 0 0 oo000 oo O
M o
o M
M M
e M M M
M M
0n oX o oM o 0
0 0 0
0 0
M~ OM 0M QM M 0%
0% 0%
0%0 0% 0%
0%
0% 0%
M 0%
0% 0%
M M
M 0%
M%0 0
% 0
% 0 0% 0 0
0 0
0 0
0 1-1- "-
-4 9
(9
(
(9 (9
(
- Data from Cookstown station ONLY after December 1996 YFAR
FIGURE C-6 MEAN QUARTERLY TLD GAMMA DOSE OYSTER CREEK GENERATING STATION, 2002 16 14H i o o
C Hm 6
.f
.~k,~\\
\\ \\~'~
g -'
I I'
!H W
k
'\\
!!!:!::!CI' !
a 4.
I rH6W I'll'
~~~~ -~----- -I
~
~
~3/4~
.O.....
L E 8
D IS T A N C E R H I N G F O M L A N 0 A p -0 2 0 J l- 0 2 0 O c t 0 2 a n -0 Firt uatelyre ul uilzed Ha sh w LD s. Se on,
hir, nd Fo rt q arerre ult uilze P na on c LN
FIGURE C-7 MEAN QUARTERLY TLD GAMMA DOSE OYSTER CREEK GENERATING STATION, 1989 - 2002
- 20 -
W 15 Li
.L
...................................................................................................... [
3 INDICATOR NEAN
- BACKGROUND MEAN I
I A
I I
I Ii I
I A
I II I
I I
.11 IN I
_N I
N I s I s I N INI N L ON 00 C%
-4 oo 00 C%
-4 o
0 N
N m
n t
t in In l
%a t-t-
00 as 0
a 0
as C,
o%
0%
ON 0%
0%
ON 0%
0%
ON O
0%
e ON 0%
ON Ch 0
0 0%
C% 0%
0%
m CN 0
0% C C%
C0 0%
m m
C 0%
0 0%
0 0
V-V-4 W
W-V4 4
-4 V-9.4
-I 4
"4 V-V-
-o N
Nq Year
-.4
-4 N
N em' o
o 0
0 0
o e
0 0
0 N
N N
IN N
- 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.
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 Left Blank D-2
TABLE D-1.1 CONCENTRATIONS OF TRITIUM IN SURFACE WATER SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2002 RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMA COLLECTION PERIOD 24 OCA QCB 04/16/02 09/11/02 MEAN'
< 101
< 102 327 t 869 510 +/- 84
< 100
< 145 214 +/- 320 306 +/- 577 122 +/- 63
- 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 04/16/02 09/11/02 MEAN' QCA 04/16/02 09/11/02 MEAN' QCB 04/16/02 09/11/02 MEAN' CONCENTRATIONS OF GAMMA EMITTERS IN SURFACE WATER SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2002 I
RESULTS IN UNITS OF PCI/LITER +/-2 SIGMA Mn-54 Co-58 Fe-59 Co-60 Zn-65
<44
<5.1
<11
<4.3
<10
< 1.91
< 2.1
< 507
< 1.67
< 3.71 3 +/-3 4 +/-4 8 +/-8 3 +/-4 7 +/-9
<2
<2
<4
<2
<3
<2
<2
<6
<2
<4 2 +/- 0 2 +/- 0 5 +/- 2 2 +/- 0 4 +/- 1
<2.1
<22
<7.8
<1.9
<62
<2.1
<4.2
<6.5
<25
<5.1 2+/-0 3+/-3 7+/-2 2+/-1 6+/-2 Zr-95
< 8 4
< 368 6 +/-7
< 3
< 4 4 +/-1
< 7.0
< 5.7 6 +/-2 Nb-95
< 5 9
< 2.8 4 +/-4
< 2
< 3 3 +/-1
< 4 4
< 3 4 +/-2 Cs-134
< 4.2
< 1.57 3 +/-4
< 2
< 2 2 +/-0
< 2 8
< 3 3 3 +/- 1 Cs-137
< 4 3
< 1.85 3 +/-3
< 2
< 2 2 +/-0
< 2 9
< 1 9 2 +/- 1 Ba-140
< 45
< 27.2 36 +/- 26
< 20
< 28 24 +/- 10
< 33
< 17.2 25 t 23 La-140
< 15
< 87 12 +/- 9
< 7
< 9 8 +/- 3
< 4 3
< 4 6 4 +/-0 0
- 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, 2002 RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMA COLLECTION PERIOD 01/01/02 - 03127/02 03/27/02 - 05/10/02 06/06/02 - 08/12/02 09/06/02 - 11/07/02 1
OCA QCB 131 +/- 55
< 98
< 131
< 151 n
< 8tj
< 97
< 131
< 161
< 100
< 136
< 137
< 184 MEAN' 128 +/- 44 119 +/- 68 140 +/- 69
- 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, 2002 RESULTS IN UNITS OF E-3 PCI/CU METER +/- 2 SIGMA STC COLLECTION PERIOD 1
01/01 - 03/27/02 03/27 - 05/10/02 06/06 - 08/12/02 09/06 - 11/07/02 MEAN*
QCA 01/01 - 03/27/02 03/27 - 05/10/02 06/06 - 08/12/02 09/06 - 11/07/02 MEAN*
QCB 01/01
- 03/27/02 03/27 - 05/10/02 06/06 - 08/12/02 09/06 - 11/07/02 Um 3
2, Mn-54 Co-58 Fe-59 Co-60 Zn-65 Zr-95 Nb-95
<5
<4
<5
<4
<5
< 10
<4
<3
<3
<8
<3
<6
<6
<4
<5
<5
<11
<5
<11
<9
<6
<1
<1
<3
<1
<2
<3
<1 5 +/- 34 36 +/- 35 68 +/- 7.0 3.4 +/- 3.1 6.2 +/- 7.5 6.7 +/- 6.5 3.9 +/- 3.9
<3
<3
<5
<3
<2
<7
<3
<2
<3
<5
<2
<5
<4
<3
<2
<2
<5
<2
<4
<4
<3
<1
<2
<4
<1
<3
<3
<2
.1 +/- 1 0 2.2 +/- 0.9 4.7 +/- 1.2 2.1 +/- 1.3 34 +/- 2 0 46 +/- 3.6 25 +/- 0 9
<4
<4
<9
<4
<9
<7
<4
<2
<1
<5
<2
<4
<2
<3
<2
<2
<5
<1
<4
<3
<3
<5
<6
<6
<4
<5
<9
<4 Cs-134
< 3
<3
<6
< 1 3.2 +/- 3.6
<3
< 2
<2
<1 2.1 +/- 1 4
<4
<2
<1
<5 m
<4
< 3
<5
< 1 3.5 +/- 3.2
<2
<3
<2
<2 2.1 +/- 0.9
<4
<2
<2
<6 Ba-140
< 14
<23
<40
< 13 22 +/- 25
< 15
< 18
<17
<22 18 +/- 55
<20
<25
<20
<39 m
La-140
< 5
< 8
<13
<4 76 +/- 83
<3
< 5
<6
<7 5 3 +/- 2.7
<7
<2
<6
< 10 6)
MEAN*
34 +/- 32 3.3 +/- 4.0 6.3 +/- 3.4 2.9 +/- 2.7 5.4 +/- 53 5.1 +/- 5.9 3.5 +/- 1.2 3.0 +/- 3.3 3.7 +/- 3.9 26 +/-18 6.1 +/-65
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES
TABLE D-111.1 STC COLLECTION PERIOD 24 04/16/02 QCA 04/16/02 QCB 04/16/02 CONCENTRATIONS OF GAMMA EMITTERS IN CLAM SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2002 RESULTS IN UNITS OF PCI/KG WET +/- 2 SIGMA K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 1410 +/- 238
< 13
<16
<34
< 14
< 32 1620 +/- 170
< 18
< 20
< 43
< 18
< 40 1307 +/- 396
< 16
< 14
< 67
< 11
< 29 Cs-134
< 11
< 19
< 19 Cs-137
< 15
< 23
< 16
-.4
TABLE D-IV.1 STC COLLECTIO]
PERIOD 24 04/16/02 09/10/02 MEAN*
QCA 04/16/02 09/10/02 MEAN*
QCB 04/16/02 09/10/02 MEAN*
CONCENTRATIONS OF GAMMA EMITTERS IN SEDIMENT SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2002 RESULTS IN UNITS OF PCI/KG DRY i 2 SIGMA N
Be-7 K-40 Mn-54 Co-58 Co-60 Cs-134
< 98 806 +/- 148
< 10
< 11
< 10
< 9
< 96 14600 +/- 455
< 9
< 10
< 8
< 8 97 +/- 3 7703 +/- 19508 10 2
10 +/- 1 9 i 2 9 +/- 2
< 115 938+/- 139 c11
< 12
< 10
< 10
< 160 1960 +/- 197
< 13
< 14
< 12
< 12 138 +/- 64 1449 +/- 1445 12 +/- 4 13 +/- 3 11 +/- 3 11 +/- 2
< 184 871 +/- 262
< 16
< 46
< 8
< 16
< 200 2656 +/- 453
< 16
< 17
< 18
< 32 192 +/- 23 1764 +/- 2524 16 +/- 0 31 +/- 41 13 +/- 14 24 +/- 23 Cs-137
< 10
< 10 10 +/- 0
< 12
< 14 13 +/- 3
< 15
< 14 15 +/- 1 0
' THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES
TABLE D-V.1 CONCENTRATIONS OF STRONTIUM AND GAMMA EMITTERS IN VEGETATION SAMPLES COLLECTED IN THE VICINITY OF OYSTER CREEK GENERATING STATION, 2002 RESULTS IN UNITS OF PCI/KG WET +/- 2 SIGMA STC COLLECTION Sr-89 Sr-90 K-40 1-131 Cs-134 Cs-137 Ba-140 La-140 PERIOD 36 CABBAGE AUGUST
< 10 5 8 +/- 08 2888 +/- 153
< 23
<5
<6
< 45
< 15 COLLARDS AUGUST
< 14 12 +/- 1.3 3820 +/- 211
< 50
< 15
< 13
< 103
< 31 MEAN*
12 +/-6 8.9 +/- 8.6 3354 +/- 1318 36 +/- 38 10 +/- 14 10 +/- 10 74 +/- 82 23 +/- 23 QCA CABBAGE AUGUST
< 20 30 +/-12 3280 +/- 171
< 28
<6
<7
< 54
< 18 COLLARDS AUGUST
< 13 57 +/-11 4720 +/- 219
< 43
< 13
< 16
< 86
< 26 MEAN*
17 +/- 10 44 +/- 3.8 4000 +/- 2036 35 +/- 22 10 +/- 10 11 +/- 11 70 +/- 45 22 +/- 12 QCB CABBAGE AUGUST
<5
<2 2479 +/- 205
<9
< 10
<7
< 29
<4 COLLARDS AUGUST
<7
<4 3937 +/- 270
<7
<9
<7
< 34
<7 MEAN' 6 +/- 3 3 +/-3 3208 +/- 2062 8 +/-4 10 +/- 1 7 +/- 1 31 +/-8 5 +/-4
- 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 ENVIRONMENTAL SERVICES (PAGE 1 OF 3)
Identification Reported Known Ratio (c)
Month/Year Number Matrix Nuclide (1)
Units Value (a)
Value (b) TBEtAnalytics Evaluation (d)
February, 2002 A15211-55 Liquid Sr-89 Sr-90 uC/mL 1.60E-03 2 03E-03 2.90E-04 3 64E-04 0 79 0 80 W
A A15213-55 Liquid H-3 uCimL 1.08E-03 1.19E-03 0 90 A
March, 2002 E3064-396 Milk Sr-89 Sr-90 pCi/L 80 83 28 27 0.96 1.04 A
A
- E3065-396 Milk 1-131 Ce-141 Cr-51 Cs-1 34 Cs-t 37 Mn-54 Fe-59 Zn-65 Co-60 pCi/L pCi 86 300 256 94 252 217 108 218 147 202 166 77 162 135 70 128 95 92 326 267 122 266 224 116 221 158 199 163 74 162 136 70 134 96 0.93 0.92 0.96 0.77 0.95 0.97 0.93 0.99 0.93 1.02 1.02 1.04 1.00 0 99 1.00 0.96 0 99 A
A A
W A
A A
A A
A A
A A
A A
A A
E3067-396 AP 1-131 Cr-51 Cs-1 34 Cs-1 37 Mn-54 Fe-59 Zn-65 Co-60 E3066-396 Charcoal 1-131 pCi 66 77 086 A
May, 2002 A15521-55 Liquid Gr-Alpha uCi/mL 8.48E-04 7.15E-04 1.19 A
A15520-55 Liquid Sr-89 Sr-90 A15522-55 Liquid Tntium uCilmL 2 63E-03 3.25E-03 2.51 E-04 2.70E-04 uCi/mL 1.35E-03 1.46E-03 0.81 0.93 0.92 A
A A
E-1
TABLE E-1 ANALYTICS ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING ENVIRONMENTAL SERVICES (PAGE 2 OF 3)
Identification Reported Known Ratio (c)
Month/Year Number Matrix Nuclide (1)
Units Value (a)
Value (b) TBE/Analytics Evaluation (d)
June, 2002 June,2002 E3220-396 Milk 1-131 Ce-141 Cr-51 Cs-1 34 Cs-1 37 Co-58 Mn-54 Fe-59 Zn-65 Co-60 pCi/L pCi 86 84 197 110 96 95 106 95 186 132 85 199 96 92 98 87 85 182 121 87 90 235 120 91 100 95 81 180 125 75 196 100 76 83 79 67 150 104 0.99 0.93 0.84 0.92 1.05 0.95 1.12 1.17 1.03 1.06 1.13 1.02 0.96 1.21 1.18 1.10 1.27 1.21 1.16 A
A A
A A
A A
A A
A A
A A
W A
A W
W A
E3222-396 AP Ce-141 Cr-51 Cs-1 34 Cs-1 37 Co-58 Mn-54 Fe-59 Zn-65 Co-60 August, 2002 A16018-55 Uquid Sr-89 Sr-90 uCi/mL 4.12E-03 4.99E-03 2.43E-04 2.64E-04 0.83 0.92 A
A A16020-55 Liquid Tritium uCi/mL 1.93E-03 2.OOE-03 uCi/mL 4.02E-03 4.99E-03 2.49E-04 2.64E-04 0.97 0.81 0.94 A
A A
September, 2002 A15989-148 Liquid E3324-396 Milk September, 2002 E3325-396 Milk Sr-89 Sr-90 Sr-89 Sr-90 1-131 Ce-141 Cr-51 Cs-1 34 Cs-137 Co-58 Mn-54 Fe-59 Zn-65 Co-60 pCi/L pCUL 106 39 84 168 210.5 127 136 93 165 90 196 147 92 39 80 160 227 132 127 97 152 89 187 149 1.15 1.00 A
A 1.05 1.05 0.93 0.96 1.07 0.96 1.09 1.01 1.05 0.99 A
A A
A A
A A
A A
A E-2
S TABLE E-1 ANALYTICS ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING ENVIRONMENTAL SERVICES (PAGE 3 OF 3)
Identification Reported Known Ratio (c)
Month/Year Number Matrix Nuclide (1)
Units Value (a) Value (b) TBE/Analytics Evaluation (d)
September, 2002 E-3327-396 Filter Ce-141 Cr-51 Cs-134 Cs-137 Co-58 Mn-54 Fe-59 Zn-65 Co-60 pCi 115 163.6 79 95 71 118 76 155 108 110 156 90 87 67 104 61 130 102 1.05 1 05 0 88 1 09 1 06 1.13 1.25 1.19 1.06 A
A A
A A
A A
A A
E3326-396 Charcoal 1-131 December, 2002 E3520-396 Milk E3521-396 Milk December.2002 E3523-396 Filter Sr-89 Sr-90 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-1 34 Cs-1 37 Co-58 Mn-54 Fe-59 Zn-65 Co-60 pCi pCiIL pCiIL pCi pci 73 85 88 68 40 38 97 136 347 97 229 143 162 80 217 172 108 370 79 226 141 152 89 196 170 86 111 346 99 220 139 142 72 178 164 128 398 114 253 160 163 83 206 189 0.86 1.29 1.05 1.13 1.23 1.00 0.98 1.04 1.03 1.14 1.11 1.22 1.05 0.84 0.93 0.69 0 89 0.88 0.93 1.07 0.95 0.90 0.88 A
W A
A W
A A
A A
A A
W A
A A
N (2)
A A
A A
A A
A E3522-396 Charcoal 1-131 84 96 (1) Only analyses performed routinely for the REMP are included on this table (2) Coincidental summing resulted in low Cesium-134 activity Eliminabon of the coincidental summing resulted in an activity of 110 pCi No further action required.
Analytics known values were inconrectly calculated Revised (as shown) evaluation was acceptable.
(a) Teledyne Brown Engineenng reported result.
(b) The Analytics known value is equal to 100% of the parameterpresent in the standard as determined by gravimetnrc and/or volumetric measurements made during standard preparation.
(c) Ratio of Teledyne Brown Engineering to Analytics results.
(d) Analytics evaluation: A= Acceptable Reported result falls within ratio limtts of 0 80-1 20. W-Acceptable with waming Reported result falls within ratio limits of 0 70-0 79 and 1 2t1-130 E-3
TABLE E-2 DOE/EML ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING ENVIRONMENTAL SERVICES (PAGE 1 OF 2)
Identification Reported Known Ratio (c)
MonthNear Number Media Nuclide (1)
Units Value (a) Value (b)
TBE/EML Evaluation (d)
June,2002 QAP 56 AP Co-60 Cs-137 Gr-Beta Mn-54 Sr-90 Bqlfilter 31.7 30.4 1.21 38.3 4.68 30.52 28.23 1.30 38.53 4.832 1.04 1.08 0.93 0.99 0.97 A
A A
A A
Soil Ac-228 Bi-212 Bi-214 Cs-137 K-40 Pb-212 Pb-214 Sr-90 Bq/kg 50 35.9 46.3 1300 608 49.4 49.1 46.6 Bqlkg 11.7 346 952 477 51.167 53.43 53.933 1326.67 621.67 51.1 54.367 53.756 11.23 313.667 864.33 586.28 0.98 0.67 0.86 0.98 0.98 0.97 0.90 0.87 1.04 1.10 1.10 0.81 A
A W
A A
A A
A A
A A
A Vegetation Co-60 Cs-1 37 K-40 Sr-90 June,2002 QAP 56 Water Co-60 Cs-1 34 Cs-1 37 Gr-Beta H-3 Sr-90 Bq/L 367 2.93 59.6 895 285 5.78 347.33 3.357 56.067 1030 283.7 7.579 1.06 0 87 1.06 0.87 1.00 0.76 A
W A
A A
W E-4
TABLE E-2 DOE/EML ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING ENVIRONMENTAL SERVICES (PAGE 2 OF 2)
Identification Reported Known Ratio (c)
Month/Year Number Media Nuclide t1)
Units Value (a) Value (b)
TBE/EML Evaluation (d)
December, 2002 QAP 57 AP Co-60 Cs-137 Gr-Beta Mn-54 Sr-90 Bq/filter 24.1 36.1 0.813 58.3 5 86 23.0 32.5 0 871 52.2 5 561 1.05 1.11 0 93 1.12 1 05 A
A A
A A
Soil Bi-212 Bi-214 Cs-1 37 K-40 Pb-212 Pb-214 Sr-90 Bq/kg 23.2 32.4 835 671 42.00 44.46 41.00 Bq/kg 11.5 345 1690 457 45 93 33.63 829.33 637.67 4343 35.2 41.16 9.66 300.67 1480 476.26 0.51 0.96 1.01 1.05 0.97 1.26 1.00 1.19 1.15 1.14 0.96 W
A A
A A
A A
A A
A A
December, 2002 QAP 57 Vegetation Co-60 Cs-137 K-40 Sr-90 Water Am-241 Co-60 Cs-1 34 Cs-1 37 Gr-Beta H-3 Sr-90 Bq/L 2.89 303 59 85.8 817 353 8.58 3.043 268.67 60.2 81.43 900 227.3 8.69 0.95 1.13 0.98 1.05 0.91 1.55 0.99 A
W A
A A
W A
(1) Only analyses performed routinely for the REMP are included on this table (a) Teledyne Brown E7gineenng reported result (b) The DOE/EML known value is equal to 100% of the parameter present in the standard as determined by gravimetno and/or volumetnc measurements made dunng standard preparation (c) Ratio of Teledyne Brown Engrneenng to DOEIEML results (d) DOEIEML evaluation A=acceptable, W=acceptable with warmng, N=not acceptable E-5
TABLE E-3 ERA ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING ENVIRONMENTAL SERVICES (PAGE 1 OF 1)
Identification Reported Known Ratio (c)
Month/Year Number Media Nuclide (1)
Units Value (a) Value (b)
TBE/ERA Evaluation (d)
May,2002 Rad 49 Water Gr-Beta Co-60 Cs-1 34 Cs-1 37 Sr-89 Sr-90 1-131 H-3 pCiIL 162 39.3 155 52.2 27.2 25.1 13.35 14600 189 39.1 17.1 52.1 31.7 28.3 14.7 17400 0.86 1.01 0 91 1.00 0 86 0.89 0.91 0.84 A
A A
A A
A A
A November, 2002 Rad 51 Water H-3 1-131 Gr-Beta Sr-89 Sr-90 Co-60 Cs-1 34 Cs-1 37 pCi/L 10100 7.94 280 41.7 6.75 122 60.0 140 10200 6.76 330 47.6 7.56 104 55.5 117 0.99 1.17 0.85 0.88 0.89 1.17 1.08 1.20 A
A A
A A
A A
A (1) Only analyses performed routinely for the REMP are included on this table.
(a) Teledyne Brown Engineenng reported result.
I(b) The ERA known value is equal to 100% of the parameter present in the standard as determined by gravimetnc and/or volumetnc measurements made dunng standard preparation (c) Ratio of Teledyne Brown Engineenng to ERA results.
(d) ERA evaluation-A=acceptable Reported result falls mwthin the Warning Limits NA=not acceptable. Reported result falls outside of the Control Limits CE=check for Error Reported result falls within the Control Limits and outside of the Waming Umit E-6
to TABLE E4 MAPEP ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING ENVIRONMENTAL SERVICES (PAGE 1 OF 1)
Identification Reported Known Month/Year Number Media Nuclide 1)
Units Value (a) Value (b)
Control Limits Evaluation (c)
March, 2002 01 -W9 Water Mn-54 Co-57 Co-60 Cs-1 34 Cs-1 37 Sr-90 Bq/L 253 141 143 26.0 270 4.71 246 143 141 28.5 286 4.8 172 20 - 319 80 100.10 - 185 90 98 70 - 183 30 19 95 - 37.05 200 20 - 371.80 3 39 - 6.24 A
A A
A A
A August, 2002 02-S9 Sotil Mn-54 Co-57 Co-60 Cs-134 Cs-137 Zn-65 K-40 Bq/kg 679 289 109 948 131 1020 722 546 246 87.5 862 ill 809 652 382.2 - 709.8 172.2 - 319.8 61.25 -113.75 603 4 -1120.6 777-144.3 556.3-1051.7 456.4 - 847.6 W
A W
A A
W A
(1) Only analyses pefformed routinely for the REMP are included on this table (a) Teledyne Brown Engineenng reported result (b) The MAPEP known value is equal to 100% of the parameterpresent in the standard as determinedbygravimetnc and/or volumetnc measurements made dunng standard preparation.
(c) DOEMAMPEP evaluation-A=acceptable, W-acceptable with warning, N=not acceptable E-7
TABLE E-5 DOE EML Cross Check Program Results for Environmental, Inc., 2002 Environmental, Inc EML Nuclide Value Uncertainty Value Min Max Agreement Lab Code Type Date (A)
(B & E)
(C & E)
(D & E)
Ratio Ratio (F)
STW-945 Water 03/01102 Co-60 349 20 +/- 2.60 347.33 0.80 - 1.20 A
STW-945 Water 03/01102 Cs-1 34 3.40 +/- 0 60 3.36 0.80 -1.30 A
STW-945 Water 03101/02 Cs-1 37 57.20 +/- 1.70 56 07 0.80 - 1.22 A
STW-945 Water 03/01/02 Sr-90 7.40 +/- 1.30 7.58 0 69 - 1.34 A
STW-946 Water 03/01/02 Gr. Beta 930 60 +/- 12.00 1030 00 0 61 - 1.43 A
STW-946 Water 03/01/02 H-3 226 30 +/- 32.70 283.70 0.78 - 2.45 A
STSO-947 Soil 03/01/02 Ac-228 55.00 +/- 5.50 51.17 0 80 -1.38 A
STSO-947 Soil 03/01/02 Bi-212 49 20 +/- 12.40 53.43 0.50 - 1.34 A
STSO-947 Soil 03/01/02 Bi-214 46.60 +/- 3 10 53 93 0.78 - 1.42 A
STSO-947 Soil 03101/02 Cs-137 1401.60 +/- 9.10 1326 67 0 80 -1.25 A
STSO-947 Soil 03101102 K-40 613.10 +/- 28.10 621.67 0.80 - 1.32 A
STSO-947 Soil 03101102 Pb-212 51.60 +/- 2 60 51.10 0.78 -1.32 A
STSO-947 Soil 03/01/02 Pb-214 52 00 +/- 3 60 54.37 0.76 - 1.46 A
STSO-947 Soil 03101/02 Sr-90 52.10 +/- 6 30 53.76 0.67 - 2.90 A
STVE-948 Vegetation 03/01/02 Co-60 13.50 +/- 2.10 11.23 0.80 -1.44 A
STVE-948 Vegetation 03/01/02 Cs-1 37 350.40 +/- 6 30 313 67 0 80 -1.31 A
STVE-948 Vegetation 03/01/02 K-40 940 80 +/- 45.60 864 33 0.79 - 1.39 A
STVE-948 Vegetation 03101/02 Sr-90 543.40 +/- 24.90 586.28 0.55 -1.21 A
STAP-949 Air Filter 03101/02 Co-60 30.10 +/- 0.30 30.52 0.80 - 1.26 A
STAP-949 Air Filter 03/01102 Cs-1 37 29.90 +/- 0 30 28 23 0.80 -1.32 A
STAP-949 Air Filter 03/01/02 Mn-54 40.40 +/- 0 40 38 53 0.80 - 1.35 A
STAP-949 Air Filter 03/01/02 Sr-90 3.40 +/- 0.40 4.83 0.53 - 1.84 A
STAP-950 Air Filter 03/01/02 Gr. Beta 1.34 +/- 0.05 1.30 0.76 - 1.36 A
STW-959 Water 09101/02 Co-60 258.40 +/- 2.30 268.67 0.80 - 1.20 A
STW-959 Water 09/01/02 Cs-1 34 50 80 +/- 3.30 60.20 0.80 -1.30 A
STW-959 Water 09/01/02 Cs-137 80 10 +/- 0.30 81.43 0 80 - 1.22 A
STW-959 Water 09/01/02 H-3 271 90 +/- 20 90 227.30 0.78 - 2.45 A
STW-959 Water 09/01/02 Sr-90 9.70 +/- 0 20 8 69 0 69 - 1.34 A
STW-960 Water 09/01/02 Gr. Beta 852.00 +/- 26 50 900.00 0.61 -1.43 A
STSO-961 Soil 09/01/02 Ac-228 47.60 +/- 1.90 42 30 0 80 - 1.38 A
STSO-961 Soil 09/01/02 Bi-212 45.60 +/- 1.70 45.93 0.50 - 1.34 A
STSO-961G Soil 09/01/02 Bi-214 48.80 +/- 4.90 33.63 0.78 - 1.42 W
STSO-961 Soil 09/01102 Cs-137 819.60 +/- 16 60 829.33 0 80 - 1.25 A
STSO-961 Soil 09/01/02 K-40 705 30 +/- 31.40 637.67 0 80 - 1.32 A
STSO-961 Soil 09/01/02 Pb-212 48 60 +/- 3.40 43.43 0.78 -1.32 A
STSO-961 Soil 09/01/02 Pb-214 51.10 +/- 5.10 35.20 0.76 - 1.46 A
STSO-961 Soil 09/01/02 Sr-90 38 50 +/- 0.10 41.16 0 67 - 2.90 A
STVE-962 Vegetation 09/01/02 Co-60 11 80 +/- 1.50 9 66 80 -1.44 A
STVE-962 Vegetation 09/01/02 Cs-1 37 340 30 +/- 16 80 30067 0.80 - 1.31 A
STVE-962 Vegetation 09/01/02 K-40 1646.00 +/- 74.40 1480.00 0.79 -1.39 A
STVE-962 Vegetation 09/01/02 Sr-90 345 60 +/- 97.80 476 26 0 55 - 1.21 A
E-8
ok TABLE E-5 DOE EML Cross Check Program Results for Environmental, Inc., 2002 Environmental, Inc.
EML Nuclide Value Uncertainty Value Min Max Agreement Lab Code Type Date (A)
(B & E)
(C & E)
(D & E)
Ratio Ratio (F)
STAP-963 Air Filter 09/01/02 Co-60 24 90 i 0 60 23.00 0.80 - 1.26 A
STAP-963 Air Filter 09/01102 Cs-137 38 00 +/- 1 30 32.50 0 80 - 1.32 A
STAP-963 Air Filter 09101/02 Mn-54 60 80 +/- 1 90 52 20 0 80 - 1.35 A
STAP-963 Air Filter 09/01102 Sr-90 5.20 +/- 0 20 5 56 0 53 - 1.84 A
STAP-964 Air Filter 09/01/02 Gr. Beta 0 80 +/- 0.10 0 87 0 76 - 1.36 A
A. Only analyses performed routinely for the REMP are included on this table.
B. The Environmental, Inc. value is the mean of 1 or 3 measurements/determinations.
C. The Environmental, Inc. uncertainty is the 2-sigma counting uncertainty for one determination and one standard deviation for three determinations.
D. The DOE EML value is the mean of replicate determinations for each radionuclide.
E. Reporting units are Bq/L for water, Bq/kg (dry) for soil, Bq/kg (wet) for vegetations and total Bq for air filters F. The control limits (min ration and max ratio are established by DOE EML. Acceptable agreement is achieved if the ratio of the Environmental, Inc. value divided by the DOE EML value falls within the control limits.
G. This naturally occuring radionuclide is present in the shield background. No follow-up actions were performed because all of the other gamma scan results were acceptable and the subject result was just outside of the upper control limit.
The control limit concept was established from percentiles of historic data distributions (1982-1992). The evaluation of this historic data and the development of the control limits are presented in DOE report EML-564.
The control limits listed in this table were developed from percentiles of data distnbution for the years 1993-1999.
E-9
TABLE E-6 ERA STATISTICAL
SUMMARY
PROFICIENCY TESTING PROGRAM FOR ENVIRONMENTAL, Inc., 2002 I
l Environmental, Inc
' ERA I
.1*
I Nuclide (A)
Value (B & El Uncertainty (C & E)
Value (D)
Min Ratio Max Ratio Agreement (El I
Lab Code Date Nuclide Value Value Mm Max Agreement (A)
(B & E)
(D' Ratio Ratio fE)
I
.4 4
4'
'4
.1.
4 STW-940 02120/02 Sr-89 53 0 +/- 2 5 55.3 466 -64 0 A
STW-940 02t20102 Sr-90 16 6 +/- 0 5 15.9
. 7.2 -246 A
STW-942 02120102 Gr. Beta 45 7 +/- 3.1 48.3 39 6 -57.0 A
STW-944 02120102 Co-60 76.9 +/- 2 7 73 4 64 7 - 82.1 A
STW-944 02120/02 Cs-134 38.7 +/- 1 6 42.1 33 4 - 50 8 A
STWVt-944 02120/02 Cs-137 92.9 +/- 2 7 88 8 80.1 -97.5 A
STW-944 02/20/02 Zn-65 361.0 +/- 9.2 359 0 298 0 -420.0 A
STW-952 05122102 Co-60 37.9 +/- 0.7 39.1 304 -47.8 A
STW-952 05122102 Cs-134 14.5 +/- 0.8 17.1 8 4 -25 8 A
STW-952 05/22102 Cs-1 37 50.0 +/- 2.0 52.1 434 -60.8 A
STW-952 05122102 Gr. Beta 171.0 +/- 2.5 189 0 140 0 -238.0 A
STW-952 05/22102 Sr-89 28.4 +/- 4 8 31.7 23 0 -40.4 A
STW-952 05/22102 Sr-90 32.4 +/- 3.1 28 3 19 6 -37.0 A
STW-953 F 05/22102 H-3 13900 0 +/- 100 0 17400 14400 20400 W
STW-954 05/22102 1-131 14.6 +/- 0.3 14.7 11.2 - 18.2 A
STW-965 08/21/02 Co-60 23 8 +/- 1.0 23 3 14.6 - 32.0 A
STW-965 08/21/02 Cs-1 34G 62.9 +/- 1.2 71.7 63.0 - 80 4 A
STW-965 08121/02 Cs-137 219.3 +/- 10.7 214 0 195.0 - 233 0 A
STW-965 08/21/02 Gr. Beta 26.7 +/- 0.4 21.9 13.2 - 30.6 W
STW-965 08/21/02 Sr-89 28 4 +/- 1.5 29 0 20.3 -37.7 A
STW-965 08121/02 Sr-90 36 5 +/- 1.1 36.4 27.7 -45.1 A
STW-965 08121/02 Zn-65 92.4 +/- 2.2 95 7 79 4 -112 0 A
STW-966 11120/02 Gr. Beta 44.7 +/- 1.0 47.0 38.3 - 55.7 A
STW-967 11120/02 H-3 10100.0 +/- 38.7 10200 8440 12000 A
STW-969 11120/02 1-131 6.0 +/- 0 4 6 8 3.3 - 10 2 A
STW-970 11/20/02 Co-60 104.0 +/-7.1 104 0 95.0 - 113.0 A
STW-970 11/20/02 Cs-134 48 2 +/- 2.3 55.5 46.8 - 64 2 A
STW-970 11120/02 Cs-137 1090 +/- 12.6 117.0 107.0 -127.0 A
STW-970 11/20/02 Gr. Beta 252.0 +/- 26.8 288.0 244 0 -416 0 A
STW-970 11120/02 Sr-89 43 2 +/- 0.7 47.6 38.9 - 56 3 A
STW-970 11120/02 Sr-90 7.5 +/- 0.2 7.6 0.0 - 16.2 A
A. Only analyses performed routinely for the REMP are included on this table.
B. The Environmental, Inc. value is the mean of 3 measurements/determinations.
C. The Environmental, Inc. uncertainty is the 2-sigma counting uncertainty for one determination and one standard deviation for three determinations D. The ERA value is equal to 100% of the parameter present in the standard as determined by gravimetric and/or volumetric measurements made during standard preparation E. A= Acceptable - Reported Result falls within the Control Umits NA = Not Acceptable - Reported Result falls outside of the Control Limits F. The analysis was repeated. result of reanalysis: 16114 +- 487 pCUIL G. ERA acknowledged an unacceptably high percentage of failure for Cs-134 and questioned its own control limits.
No problems were Identified In the analysis.
E-1 0
TABLE E-7 MAPEP Cross Check Program Results for Environmental, Inc., 2002 Environmental, Inc.
MAPEP Nucide Value Uncertainty Value Min Max Agreement Lab Code Type Date (A)
(B & E)
(C & E)
(D & E)
Ratio Ratio (F)
STW-939 STW-939 STW-939 STW-939 STW-939 STW-939 STW-939 STSO-955 STSO-955 STSO-955 STSO-955 STSO-955 STSO-955 water water water water water water water 12101/01 12/01/01 12/01/01 12/01/01 12/01101 12101101 12/01/01 Co-57 Co-60 Cs-134 Cs-137 Mn-54 Sr-90 Zn-65 Co-57 Co-60 Cs-134 Cs-137 Mn-54 Zn-65 1389 +/-05 139.1 +/-05 25 16 +/-02 279 96 +/- 0.9 253.64 +/- 0 9 4 88 +/- 0.3 706 +/- 1.1 21058 +/-20 84 38 +/-09 6926 +/-2.1 96 98 +/- 1.7 50974 +/-34 78359 +/-64 143 +/- 14.3 141 +/- 14.1 28 5 +/-0 3 286 i28 6 246 +/-02 48 +/-05 67.3 +/- 6.7 246 +/- 24.6 87.5 +/-88 862 +/- 86.0 11t +/-11.1 546 +/- 54.6 809 +/- 80.9 100.1 - 185 9 98.7 - 183.3 1995 -37.1 200.2 - 371 8 172.2 - 319 8 3.36 -62 47.11 - 87 5 172.2 - 319 8 61.25 - 113.8 603 4 - 1120.6 77.7 - 144.3 382 2 - 709 8 566 3 - 1051.7 soil soil soil soil soil soil 10116/02 10/16/02 10/16/02 10/16/02 10/16/02 10/16/02 A. Only analyses performed routinely for the REMP are included on this table.
B. The Environmental, Inc. value is the mean of 1 or 3 measurements/determinations.
C. The Environmental, Inc. uncertainty is the 2-sigma counting uncertainty for one determination and one standard deviation for three determinations.
D. The DOE EML value is the mean of replicate determinations for each radionuclide.
E. Reporting units are Bq/L for water, Bqlkg (dry) for soil, Bqlkg (wet) for vegetations and total Bq for air filters F. The control limits (min ration and max ratio are established by DOE EML. Acceptable agreement is achieved if the ratio of the Environmental. Inc. value divided by the DOE EML value falls within the control limits.
E-1 1