ML071590393
| ML071590393 | |
| Person / Time | |
|---|---|
| Site: | Calvert Cliffs  |
| Issue date: | 05/10/2007 |
| From: | Sanders S R Constellation Energy Group |
| To: | Document Control Desk, Office of Nuclear Reactor Regulation |
| References | |
| Download: ML071590393 (113) | |
Text
Calvert Cliffs Nuclear Power Plant Constellation Generation Group, LLC 1650 Calvert Cliffs Parkway Lusby, Maryland 20657 0 Constellation Energy May 10, 2007 U. S. Nuclear Regulatory Commission Washington, DC 20555 ATTENTION:
SUBJECT:
Document Control Desk Calvert Cliffs Nuclear Power Plant; Unit Nos. I & 2; Docket Nos. 50-317 & 50-318 Independent Spent Fuel Storage Installation; Docket No. 72-8 Annual Radiological Environmental Operating Report
REFERENCES:
(a) Calvert Cliffs Nuclear Power Plant Technical Specification 5.6.2 (b) Calvert Cliffs Independent Spent Fuel Storage Installation Technical Specification 6.2 In accordance with References (a) and (b), Calvert Cliffs Nuclear Power Plant is submitting the Annual Radiological Environmental Operating Report, for the calendar year 2006.Should you have questions regarding this matter, please contact Mr. Jay S. Gaines at (410) 495-5219.S/ry truly yours, Steven R. Sanders General Supervisor
-Chemistry SRS/CAN/bjd
Attachment:
As stated cc: D. V. Pickett, NRC S. J. Collins, NRC Resident Inspector, NRC R. I. McLean, DNR R. Manley, MDE ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT FOR THE CALVERT CLIFFS NUCLEAR POWER PLANT UNITS 1 AND 2 AND THE INDEPENDENT SPENT FUEL STORAGE INSTALLATION January 1 -December 31, 2006 A. M. Barnett L. J. Bartal, Ph.D.B. D. Nuse CONSTELLATION ENERGY CONSTELLATION GENERATION GROUP, LLC APRIL 2007 (LEFT BLANK)
January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE OF CONTENTS LIST O F FIG URES ...........................................................................................................................
iii LIST O F TABLES ...............................................................................................................................
v I. SUM M ARY .......................................................................................................................................
1 II. CALVERT CLIFFS NUCLEAR POWER PLANT RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ............................................................
3 II.A. INTRODUCTION
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3 II.B. PROGRAM .............................................................................................................................................................
3 II.B .1 O b e iectiv es .......................................................................................................................................................
3 II.B.2 Sample Collection
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4 II.B3.3 Data Interpretation
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4 II.B P.4 Program Exceptions
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4 II.C. RESULTS AND DISCUSSIONS
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4 II.C.1 Aquatic Environment
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5 I.C.l.a Bay W ater ...................................................................................................................................................
5 II.C.l.b Aquatic Organisms
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5 II.C..c Shoreline Sediment .....................................................................................................................................
5 II.C.2 Atmospheric Environment
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! ..........................................................................................................
8 II.C.2.a Air Particulate Filters ................................................................................................................................
8 II.C.2.b Air Iodine .......................................................................................................
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8 II.C.3 Terrestrial Environment
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8 II.C.3.a Vegaetation
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10 II.C.4 Direct Radiation
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10 II.D. CONCLUSION
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12 III. INDEPENDENT SPENT FUEL STORAGE INSTALLATION RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ......................................................
21 III.A. INTRODUCTION
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21 III.B. PROGRA M .........................................................................................................................................................
21 III.B.1 Objectives
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21 III.B.2 Sample Collection
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22 III.B.3 Data Interpretation
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22 1II.B.4 Program Exceptions
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- ............................
22 III.C. RESULTS AND DISCUSSIONS
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22 III.C.1 Atmospheric Environment
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22 III.C. a Air Particulate Filters .............................................................................................................................
22 III.C.2 Terrestrial Environment
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23 III.C.2.a Veeetation
................................................................................................................................................
23 III.C .2 .b S oils ..........................................................................................................................................................
2 3 III.C.3 Direct Radiation
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24 III.D. CONCLUSION
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24 IV. REFERENCES
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28 APPENDIX A Sample Locations for the REMP and the ISFSI .............................................
29 APPENDIX B Analysis Results for the REMP and the ISFSI .................................................
45 APPENDIX C O uality Assurance Program ........................................................................
...........
69 APPENDIX D Land Use Survey ...........................................
87 APPENDIX E Additional Samples and Analysis Results ........................................................
89 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK)ii January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 LIST OF FIGURES Figure Title Page 1 Tritium in Chesapeake Bay W ater ......................................................................................
6 2 Silver-i 10m and Potassium-40 in Chesapeake Bay Oysters ..............................................
7 3 Nuclear Fallout in the Calvert Cliffs Area ...........................................................................
9 4 Mean TLD Gamma Dose, Calvert Cliffs Nuclear Power Plant ...............................................
11 5 Atmospheric Dispersion Around CCNPP Average Relative Air Concentrations
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15 6 Atmospheric Dispersion Around CCNPP Average Relative Ground Deposition
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17 7 M ean TLD Gam m a Dose, ISFSI .........................................................................................
25 A-1 Map of Southern Maryland and Chesapeake Bay Showing Location of Calvert Cliffs N uclear Pow er Plant ............................................................................................................
35 A-2 Calvert Cliffs Nuclear Power Plant Sampling Locations, 0-2 Miles ..................................
37 A-3 Calvert Cliffs Nuclear Power Plant Sampling Locations, 0-10 Miles ................................
39 A-4 Independent Spent Fuel Storage Installation Sampling Locations
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42 A-5 Enlarged Map of the Independent Spent Fuel Storage Installation Sampling Locations
........ 43 iii January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK)iv January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 LIST OF TABLES Table Title Page 1 Synopsis of 2006 Calvert Cliffs Nuclear Power Plant Radiological Environmental M onitoring Program ............................................................................................................
19 2 Annual Summary of Radioactivity in the Environs of the Calvert Cliffs Nuclear Plant U nits 1 and 2 ...........................................................................................................................
20 3 Synopsis of 2006 Calvert Cliffs Nuclear Power Plant Independent Spent Fuel Storage Installation Radiological Environmental Monitoring Program ..........................................
26 4 Annual Summary of Radioactivity in the Environs of the Calvert Cliffs Nuclear Power Plant Independent Spent Fuel Storage Installation
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27 A-1 Locations of Environmental Sampling Stations for the Calvert Cliffs Nuclear Power Plant..33 A-2 Locations of Environmental Sampling Stations for the Independent Spent Fuel Storage Installation at Calvert C liffs ...........
\ ..................................................................................
41 B-i Concentration of Tritium and Gamma Emitters in Bay Water ..........................................
49 B-2 Concentration of Gamma Emitters in the Flesh of Edible Fish ..........................................
50 B-3 Concentration of Gamma Emitters in Oyster Samples ......................................................
51 B-4 Concentration of Gamma Emitters in Shoreline Sediment .................................................
52 B-5 Concentration of Iodine- 1-31 in Filtered Air ......................................................................
53 B-6 Concentration of Beta Emitters in Air Particulates
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55 B-7 Concentration of Gamma Emitters in Air Particulates
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59 B-8a Concentration of Gamma Emitters in Vegetation Samples ......................
60 B-8b Concentration of Gamma Emitters in Vegetation From Locations Around the IFSFI ..... 61 B-9 Concentration of Gamma Emitters in Soil Samples From Locations Around the ISFSI ........ 62 B-10 Typical MDA Ranges for Gamma Spectrometry
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63 B-11 Typical LLDs for Gamma Spectrometry
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64 B -12 D irect R adiation .......................................................................................................................
65 C-1 Results of Participation in Cross Check Programs .............................................................
73 C-2 Results of Quality Assurance Program ................................................................................
76 C-3 Teledyne Brown Engineering's Typical MDAs for Gamma Spectrometry
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85 D -i L and U se Survey ......................................................................................................................
87 E-1 Locations of Non-Tech Spec Environmental Sampling Stations for Calvert Cliffs Nuclear P ow er P lant ..............................................................................................................................
92 E-2 Synopsis of 2006 Calvert Cliffs Nuclear Power Plant Non-Tech Spec Radiological Environmental Monitoring Program ..................................................................................
93 E-3 Annual Summary for Calvert Cliffs Nuclear Power Plant Units 1 & 2 Non-Tech Spec Radiological Environmental Monitoring Program .............................................................
94 E-4 Concentration of Gamma Emitters in Bottom Sediment ...................................................
95 E-5 Concentration of Iodine- 131 in Filtered Air ......................................................................
96 E-6 Concentration of Beta Emitters in Air Particulates
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98 V January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 LIST OF TABLES -Continued Table Title Page E-7 Concentration of Gamma Emitters in Air Particulates
..........................................................
100 E-8 Concentration of Tritium and Gamma Emitters in Taylors Island Well Water .....................
101 E-9 Direct Radiation as Measured in Pressurized Ion Chamber ..................................................
102 E -10 D irect R adiation .....................................................................................................................
103 E-il Direct Radiation from Resin Storage Area ............................................................................
104 vi January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 I.
SUMMARY
During this operating period for Calvert Cliffs Nuclear Power Plant (CCNPP) Units 1 and 2, a total of 3592 radiological analyses were performed and the analytical results reviewed.
Most of these analyses were performed to satisfy the requirements of the Offsite Dose Calculation Manual (ODCM) (Ref. 6) and the Environmental and Independent Spent Fuel Storage Installation (ISFSI) Technical Specifications (Ref. 10). Some of these samples, although not required by either the ODCM or the Technical Specifications, were collected to maintain our commitments to the surrounding community and to maintain historical continuity of the CCNPP Radiological Environmental Monitoring Program (REMP) that started in 1970. The entire monitoring program in place around CCNPP is divided into three parts: the original REMP, the ISFSI monitoring program, and the Non-ODCM Radiological Environmental Monitoring.
The following paragraphs describe each of these parts in more detail.A total of 654 radiochemical analyses were performed on 586 environmental samples and 537 thermoluminescent dosimeters (TLDs) were analyzed for ambient radiation exposure rates as part of the original REMP. These analyses were performed to satisfy the requirements of the ODCM (Ref. 6) and the Environmental Technical Specifications (Ref. 5).For the ISFSI monitoring program, 357 radiochemical analyses were performed on 297 environmental samples, 52 of which were in common with the original REMP. In addition, 480 TLDs, 24 in common with the original REMP, were analyzed for ambient radiation exposure rates. These analyses were performed to satisfy the requirements of the ODCM (Ref. 6) and the ISFSI Technical Specifications (Ref. 10).In addition, 583 analyses were performed on 535 additional environmental samples, and 480 additional TLDs were analyzed for ambient radiation exposure rates. Also, six pressurized ion chambers continuously monitored the environs around the plant for ambient radiation levels resulting in 72 monthly measurements.
As mentioned earlier, these additional analyses reflect a commitment to maintain historical continuity for samples and sampling pathways discontinued from the program when the Environmental Technical Specifications were changed in March 1985 and to satisfy monitoring commitments made to the surrounding community.
And lastly, 200 radiochemical analyses were performed on 200 quality assurance samples and 132 quality assurance TLDs were analyzed as part of an internal and external quality assurance program associated with Teledyne Brown Engineering.
Laboratory intercomparison samples obtained from Environmental Resource Associates (ERA) and Analytics' Inc. were also analyzed.Samples collected from the aquatic environment included bay water, fish, oysters, and shoreline sediment.
Bay water was analyzed for tritium and gamma emitters.
Fish, oysters, and shoreline sediments were analyzed for gamma emitting radionuclides.
I January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Monitoring the atmospheric environment involved sampling the air at various locations sur-rounding CCNPP and the ISFSI. Air particulates and gaseous iodine were collected on glass fiber filters and silver zeolite molecular sieve cartridges, respectively.
The particulate filters were analyzed for beta activity and gamma emitting nuclides.
The molecular sieve cartridges were analyzed for airborne gaseous radioiodine.
Samples from the terrestrial environment consisted of vegetation and soil samples collected and analyzed for gamma emitters.
Vegetation samples for the original REMP were also analyzed for 1-131.Measurements of direct radiation, as required by the ODCM, were performed by analyzing TLDs from forty locations surrounding CCNPP and the ISFSI.Natural radioactivity was detected in essentially all 3592 radiological analyses performed.
Low levels of man-made fission products were also observed in 17 of these analyses.
All of these observations were attributed to fallout from past atmospheric weapons testing. Detailed discussions about the results of these analyses are contained in the body of this report.To assess the plant's contribution to the radiation levels of the ambient environment, dose calculations were performed using the plant's effluent release data, on-site meteorological data, and appropriate pathways.
The results of these dose calculations indicate: a. a maximum thyroid dose of 5.16 x 10-2 mrem via liquid and gaseous pathways, which is less than 0.1% of the acceptable limit of 75 mrem/yr as specified in 40CFR190;b. a maximum whole body dose of 3.81 x 10-3 mrem via liquid and gaseous pathways, which is less than 0.02% of the acceptable limit of 25 mrem/yr as specified in 40CFR190;c. a maximum calculated dose to all other organs via liquid and gaseous pathways was equal to 1.00 x 10-2 mrem to the skin. This dose isless than 0.05% of the allowable limit of 25 mrem/yr as specified in 40CFR190.Thus, it is concluded based upon the levels of radioactivity observed and the various dose calculations performed, that CCNPP Units I and 2 and the ISFSI did not cause any significant radiological impact on the surrounding environment.
2 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 II. CALVERT CLIFFS NUCLEAR POWER PLANT RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM II.A. INTRODUCTION Constellation Energy (CE), previously known as Baltimore Gas and Electric Company (BGE), has been conducting a REMP in the environs of the CCNPP since the summer of 1970. The Calvert Cliffs site is an operating nuclear generating station consisting of two pressurized water reactors.
Unit 1 achieved criticality on October 7, 1974 and commenced commercial operation in May 1975. Unit 2 achieved criticality on November 30, 1976 and went into commercial operation April 1, 1977. The location of the plant in relation to local metropolitan areas is shown on Figure A-i.Results of the monitoring program for the pre-operational period have been reported in a series of documents (Ref. 1-4). The results from previous operational periods are contained in annual reports submitted to the NRC as required.Results of the monitoring program for the current operational period are included in this-report.
The report presents the content of the REMP (Table 1), the sampling locations (Appendix A), the summary of the analytical results (Table 2), a compilation of the analytical data (Appendix B), the results of the Analytics Intercomparison Program and the Quality Assurance Program (Appendix C), the results of the Land Use Survey (Appendix D), and a compilation of the analytical data for extra samples collected (Appendix E). Interpretation of the data and conclusions are presented in thebody of the report.The environmental surveillance data collected during this reporting period were compared with that generated in previous periods whenever possible to evaluate the environmental radiological impact of CCNPP Units I and 2.ll.B. PROGRAM II.B.1 Obeectives The objectives of the REMP for the Calvert Cliffs Nuclear Power Plant are: a. To verify that radioactivity and ambient radiation levels attributable to plant operation are within the limits specified in the ODCM (Ref. 6) and the Environmental Radiation Protection Standards as stated in 40 CFR Part 190, b. To detect any measurable buildup of long-lived radionuclides in the environment, c. To monitor and evaluate ambient radiation levels, d. To determine whether any statistically significant increase occurs in the con-centration of radionuclides in important pathways.3 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 II.B.2 Sample Collection The locations of the individual sampling stations are listed in Table A-i and shown in Figures A-2 and A-3. All samples were collected by contractors to, or personnel of Constellation Energy according to CCNPP Procedures (Ref. 7,12).II.B.3 Data Interpretation Many results in environmental monitoring occur at or below the minimum detectable activity (MDA). In this report, all results at or below the relevant MDA are reported as being "less than" the MDA value.II.B.4 Program Exceptions There was a program exception during this operating period. Samples of collards (sample codes IbI and Ib7), cabbage (sample codes Ib2 and Ib8), and broccoli (sample codes Ib3 and Ib9) were not taken from the garden locations Bay Breeze Road and the EOF during the month of August as required by the ODCM (Ref. 6). No substitute samples were collected from the natural vegetation around the locations in lieu of the samples not taken from these locations in the August sampling period. This program exception has been entered into the site's Corrective Action Program to ensure it does not recur.II.C. RESULTS AND DISCUSSIONS All the environmental samples collected during the year were analyzed using Constellation Energy laboratory procedures (Ref. 8). The analytical results for this reporting period are presented in Appendix B and are also summarized in Table 2. For discussion, the analytical results are divided into four categories.
The categories are the Aquatic Environment, the Atmospheric Environment, the Terrestrial Environment, and Direct Radiation.
These categories are further divided into subcategories according to sample type (e.g., Bay Water, Aquatic Organisms, etc., for the Aquatic Environment).
4 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 II.C.1 Aquatic Environment The aquatic environment surrounding the plant was monitored by analyzing samples of bay water, aquatic organisms, and shoreline sediment.
These samples were obtained from various sampling locations on the Chesapeake Bay near the plant.II.C.l.a Bay Water Monthly bay water samples were taken from two locations during the year. These locations are the Intake Area (sample code Wal) and the Discharge Area (sample code Wa2). Composite samples were obtained from each location for the entire sampling period. These samples were analyzed for tritium and gamma emitters.The tritium analyses, performed on quarterly composites of the monthly bay water samples, revealed no evidence of tritium in any of the samples taken from either site throughout the year.Figure 1 compares tritium observed in the plant discharge and intake with annual effluent releases as reported in the Radioactive Effluent Release Report.Monthly analyses of bay water samples from both locations for gamma emitters exhibited no detectable concentrations of any plant-related radionuclides.
II.C.l.b Aquatic Organisms Twelve samples of aquatic organisms were obtained from four locations during the year.Samples of fish, when in season, are normally collected from the Discharge Area (sample codes lal and Ia2) and from the Patuxent River (sample codes Ia4 and Ia5). As shown in Table B-2, two species of fish were sampled at both the plant discharge and the control point in the Patuxent River. Oyster samples were obtained quarterly from Camp Conoy (sample code Ia3) and Kenwood Beach (Ia6).Edible portion of the fish and oyster samples were analyzed for gamma emitters.
Gamma spectrometric analyses of the fish exhibited naturally occurring K-40, but no detectable concentrations of any plant-related radionuclides.
Oyster samples likewise exhibited naturally occurring K-40, but no detectable concentrations of any plant related radionuclides.
II.C.l.c Shoreline Sediment Semiannual shoreline sediment samples were taken from one location during the year. This location is Shoreline at Barge Road (sample code Wbl). The samples obtained from this location were analyzed for gamma emitters.Gamma spectrometric analyses of these samples exhibited naturally occurring radionuclides, but no detectable concentration of any plant-related radionuclides.
5 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 FIGURE 1 Tritium in Chesapeake Bay Water I.I-1200 1000 800 600 400 -200~Ii~ii thu i~ I ut ii I I Ii 111111111 IIIIIIIII I IIIII III I IIIIIIIIIIIIIIIII I IIIII III I I I III I IIII I III 0 2000 1800 1600 1400 1200 1000 800 600 400 200 0 IIý4 1. i ý, J1 1, 1 JI I 5; 8 8 ~ 8 5; 8 8 2000 1800 1600 1400 1200 1000 800 600 400 200 0 6 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 FIGURE 2 Silver-1Orm and Potassium-40 in Chesapeake Bay Oysters 0.2 0.18 0.16 0,14 0.12 0.1 , -0.0 c0.06 S0.04 0.02 0 7000-6000 5000 4000 30002000 0 7000 I 6000 7000 4000 3000 -.2000 1000 11, Ij.I I II I 1 Ii i 1 1i i i 1 .I S ~ 8 ~ 8 ll Rd, h .I .ý. .. 11L I-lImmBII I .... I l i m Ill l l-, A l.... -.. 11 .. , it l l0 fl 8 81 9 S 83 8a 8 8 7 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 II.C.2 Atmospheric Environment The atmospheric environment was monitored by analyzing air particulate filters and silver zeolite cartridges (for trapping radioiodine species).
These samples were collected from five locations surrounding the plant. These locations are On Site before the Entrance to Camp Conoy (sample code Al), Camp Conoy Road at the Emergency Siren (sample code A2), Bay Breeze Road (sample code A3), Route 765 at Lusby (sample code A4), and at the Emergency Operations Facility (sample code A5).II.C.2.a Air Particulate Filters Weekly composite air particulate filter samples were collected from the five locations during the year. These samples were analyzed for beta activity and gamma emitters.Weekly analyses for beta activity on air particulate filters collected from all five locations showed values characteristic of background levels. The values ranged from 0.8 x 10-2 to 4.4 x 10-2 pCi/m 3 for the indicator locations and 1.0 x 10-2 to 4.0 x 10-2 pCi/m 3 at the control lo-cation. The location with the highest overall mean of 2.1 x10-2 pCi/m 3 was A5, Emergency Operations Facility (EOF).Gamma spectrometric analyses of monthly composited air particulate samples exhibited no detectable concentrations of any plant-related radionuclides in any of these samples. Naturally occurring radionuclides, such as Be-7, were detected in nearly all samples.Figure 3 depicts the historical trends of beta activity.II.C.2.b Air Iodine Weekly composited silver zeolite cartridges (for trapping radioiodine species) were collected from the five locations during the year. These samples were analyzed for radioiodine species.Weekly radioiodine analyses of silver zeolite cartridges collected from all five locations ex-hibited no detectable concentrations of 1- 131.Figure 3 depicts the historical trends of radioiodine.
II.C.3 Terrestrial Environment The terrestrial environment was monitored by analyzing samples of vegetation collected monthly, when available, from various sampling locations near the plant during the normal growing season.8 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 FIGURE 3 Nuclear Fallout in the Calvert Cliffs Area SURFACE AIR VAPORS, LUSBY, MD (A4)250 200 oe)E C 150 C" 100 8 Ct'50 0 4 1200 C 1000 0 1200 E 800 600 (-(5 200 0 ATMOSPHERIC FALLOUT W) co Q qW c 0 aN W(00 P- r- W 00W W M M0 ATMOSPHERIC FALLOUT From weapons testing ATMOSPHERIC FALLOUT From weapons testing ATMOSPHERI FALLOUT Froi Chemobyl m.1.I II r) r- C) M-(~ Ul) r-- 0) V ) U) r- 0) V C) 10 1'-r-- I- co Go co 00 C) 0 ) C) 0) C) 0 0 0 0 9 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 II.C.3.a Vegetation Vegetation samples were collected from three locations during the year. These locations are Garden Plot off Bay Breeze Road (sample codes IbI, Ib2, and Ib3), On Site before the Entrance to Camp Conoy (sample codes Ib4, Ib5, and Ib6), and the Emergency Operations Facility (sample codes Ib7, Ib8, and Ib9). These samples were analyzed for gamma emitters, including analyses for 1-13 1.All samples showed detectable amounts of naturally occurring K-40 and Be-7. No plant related radionuclides were found in any of these samples.II.C.4 Direct Radiation Direct radiation is measured by a network of TLDs in each overland sector surrounding the Plant both at the plant boundary and at 4 miles from the Plant.TLDs were collected quarterly from twenty-three locations surrounding the plant. The twenty indicator locations are On Site Along the Cliffs (sample code DRI), Route 765 Auto Dump (sample code DR2), Giovanni's Tavern (sample code DR3), Route 765 across from White Sands (sample code DR4), John's Creek (sample code DR5), Lusby (sample code DR6), On Site before the Entrance to Camp Conoy (sample code DR7), On Site at Emergency Siren (sample code DR8), Bay Breeze Road (sample code DR9), Decatur and Calvert Beach Roads (sample code DR1O), Dirt Road off Mackall and Parran Roads (sample code DRI 1), Mackall and Bowen Roads (sample code DR12), Wallville (sample code DR13), Rodney Point (sample code DR14), Mill Bridge and Turner Roads (sample code DR15), Appeal School (sample code DR16), Cove Point and Little Cove Point Roads (sample code DR17), Cove Point (sample code DR18), Long Beach (sample code DR19), and On Site Near Shore (sample code DR20). The three control locations are the Emergency Operations Facility (sample code DR21), Solomons Island (sample code DR22), and Taylors Island, Carpenters Property (sample code DR23).The mean 90 day ambient radiation measured at the indicator locations was 11.36 mR and ranged from 9.29 to 15.00 mR as reported in Table 2. The control locations showed a 90 day mean of 12.62 mR with ranges from 10.17 to 15.46 mR. The location with the highest overall mean of 15.00 was DR23, Taylors Island, which ranged from 14.41 to 15.46 mR. A comparison of the means and ranges of the current TLD data with those of both the historical data and the regional data shows no plant-related contribution to the measured direct radiation exposure.Figure 4 shows the historical comparison of the average monthly radiation levels per calendar year for TLDs on site, at four miles, and at the control locations.
10 0'0(1 o CI UN 0 c0 coO V-- 0-G a..016 z ait 0 EU E 0 o U)m S&P ocki0 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Il.D. CONCLUSION No man-made fission or activation by-products attributable to plant operations were observed in the environment surrounding the plant during the year.Historical trends for tritium in bay water, Ag- I1Oim and K-40 in oyster samples, nuclear fallout in the Calvert Cliffs area, and TLD data are depicted in Figures 1 through 4. As can be seen from these figures, the plant made no adverse radiological contributions to the surrounding environment.
To assess the plant's contribution to the ambient radiation levels of the surrounding environment, dose calculations were performed using the plant's effluent release data, on site meteorological data (see X/Q and D/Q values presented in Figures 5 and 6), and appropriate pathways.
The results of these dose calculations indicate: Gaseous Pathways A maximum thyroid dose of 4.90 x 10-2 mrem to a child via the plume, ground, vegetable, meat, and inhalation pathways at 2.1 km SE of the containments at Calvert Cliffs. This is less than 0.1% of the acceptable limit of 75 mrem/yr as specified in 40CFR190, "Environmental Radiation Protection Standards for Nu-clear Power Operations." A maximum whole body gamma dose of 2.2 x 10-3 mrem to a child at 2.4 km SSW of the containments at Calvert Cliffs. This is less than 0.01% of the acceptable dose limit of 25 mrem/yr as specified in 40CFR190.A maximum dose to any other organ, in this case the'skin, of 1.00 x 10-2 mrem to a child at 1.8 km SSW of the containments at Calvert Cliffs. This is less than 0.05% of the acceptable dose limit of 25 mrem/yr as specified in 40CFR190.Liquid Pathways A maximum thyroid dose of 2.6 x 10-3 mrem to an adult for all liquid pathways, which is about 0.00 1% of the acceptable dose limit of 75 mrem/yr as specified in 40CFR190.A maximum whole body dose of 1.61 x 10-3 mrem to a child via all liquid pathways, which is less than 0.01% of the acceptable dose limit of 25 mrem/yr as stated in 40CFR190.A maximum dose to any other organ, in this case bone, of 4.57 x 10-3 mR to a child for all pathways, which is 0.02% of the acceptable dose limit of 25 mrem/yr specified in 40CFR190.12 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Gaseous and Liquid Pathways Combined A maximum thyroid dose of 5.16 x 10-2 mrem via liquid and gaseous pathways, which is less than 0.1% of the acceptable limit of 75 mrem/yr as specified in 40CFR 190;A maximum whole body dose of 3.81 x 10-3 mrem via liquid and gaseous pathways, which is less than 0.02% of the acceptable limit of 25 mrem/yr as specified in 40CFR190;A maximum calculated dose to all other organs via liquid and gaseous pathways was equal to 1.00 x 10-2 mrem to the skin. This dose was less than 0.05% of the allowable limit of 25 mrem/yr as specified in 40CFR190.In all cases, the calculated doses are a small fraction of the applicable limits specified in 40 CFR Part 190.Therefore, it is concluded that the operation of Calvert Cliffs Units 1 and 2 produced radioactivity and ambient radiation levels significantly below the limits of the ODCM and 40 CFR Part 190, and there was no significant buildup of plant-related radionuclides in the environment due to the operation of the CCNPP.13 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK)14 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 FIGURE 5 Atmospheric Dispersion Around CCNPP Average Relative Air Concentrations AILUERT CLIFFS 04/13/8?B0s1B HE INTEGRATED ELEUArTED AUERAGE X/Q 3.55 HOUR INttEGRrION;RELERE t IPnieLr IE..88 HL-5 MIODEL: TIME INTEGRATED STRA[GHT LINE________________________________________________
START DOSE INTEGRATION-01/01/G 01 .00 END DOSE INTEGRAT'ION!
12/31/OG 24080 SITUE C TITLEU TI!ERIODD,64:
COENTOUR LEGEND 1 3-4-KSEC/M3)4-1E-87t 2.@E 4.BE-07 1.@E-I7-2.SE-07
?.IE-IS9-1
.0E- 7 4. IE- --7.* OE-1 .E-I6-2.OE-15 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK)16 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 FIGURE 6 Atmospheric Dispersion Around CCNPP Average Relative Ground Deposition ALUERT CLIFFS 0411310 IE INTEGRATED DEPOSIrIoN Dig UuqQr Z.IM MODEL: TIME INTEGRATED STRAIGHT LINE_STRT DOSE INTEGRATIQN:
101/811G 8 1t88 END DOSE INTEGRAl 1iN. I2/31/BS 24!00 SITE- CI TITLE: TIf PERIOD:S643 1!OT:NUI LEGEND 4-5p 4.I:E -049*2.@E- g- -11E-09?.IE-Ig-1.BE-09
- 4. ZE- --7 O E-10 2.UE-1I-4.SE-10 1.IE-18-2.OE-10
?.:IE-11 -1 OSE-10 4.UE-11 -7.SE-11 2.IE 4.OE-11 17 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK)18 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table 1 Synopsis of 2006 Calvert Cliffs Nuclear Power Plant Radiological Environmental Monitoring Program Sample Type Sampling Frequency Number of Locations Number Collected Analysis Analysis Frequency 1 Number Analyzed Aquatic Environment Bay Water Fish2 Oysters Shoreline Sediment Atmospheric Environment Air lodine 3 Air Particulates 4 Direct Radiation Ambient Radiation Terrestrial Environment MC A Q SA 2 4 2 1 24 4 8 2 Gamma H-3 Gamma Gamma Gamma M QC 24 8 A Q 4 8 2 SA W W 5 5 257 258 1-131 Gross Beta W 257 258 W Gamma MC 60 Q 23 537 TLD Q 537 Vegetations M 3 30 Gamma M 30 W-weekly, M=monthly, Q=quarterly, SA=semiannual, A=annual, C=composite 2 Once in Season, July through September 3 The collection device contains silver Zeolite 4 Beta counting is performed after >72 hour decay, Gamma spectroscopy performed on monthly composites of weekly samples'Monthly during growing season when available 19 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table 2 Annual Summary of Radioactivity in the Environs of the Calvert Cliffs Nuclear Power Plant Units 1 and 2 Medium or Pathway Sampled (Unit of Measurement)
Type and Total Number of Analyses Performed Lower Limit of Detection (LLD)Indicator Locations Mean (F)/Range 1 Location with Highest Annual Mean Name/Distance
&Direction 2 Highest Annual Mean (F) / Range 1 Control Locations Mean (F)/Range Atmospheric Environment Air Gross Beta (258) 0.5 1.7 (206/206)
EOF A5 2.1 (52/52) 2.1 (52/52)Particulates (0.8-4.4) 19.3 km WNW (1.0-4.0)
(1.0-4.0)(10-2 pCi/m 3)Direct Radiation Ambient TLD (537) -- 11.36 (471/471)
Taylors Island 15.00 (24/24) 12.62 (66/66)Radiation (9.29-15.00)
DR23 (14.41-15.46)
(10.17-15.46)(mRJ90 days) 12.6 km ENE' Mean and range based upon detectable measurements only. Fraction (F) of detectable measurements at specified location is indicated in parentheses 2 From the centerpoint between the two containment buildings.
20 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 III. INDEPENDENT SPENT FUEL STORAGE INSTALLATION RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM III.A. INTRODUCTION In August 1990 BGE initiated a program of additional radiological environmental monitoring around the site for the Independent Spent Fuel Storage Installation (ISFSI). The first dry fuel storage canister was loaded into the ISFSI in November of 1993, with more canisters being loaded in subsequent years. During this operating period, three additional canisters of spent fuel were transferred to the ISFSI. Area was also used as a temporary storage area for additional radioactive material.Results of the monitoring program for the ISFSI for the current period are included in this:report.
This report presents the content of the ISFSI REMP (Table 3), the ISFSI sampling locations (Appendix A), the summary of the analytical results of the period (Table 4), and a compilation of the analytical data for the period (Appendix B). Interpretation of the data and conclusions are presented in the body of the report.The ISFSI monitoring program is as described in this section of the report. Pressurized Ion Chambers (PICs), because they duplicate direct surveillance by TLDs and because they experience problems with reliability, were excluded from the Technical Specification portion of the ISFSI monitoring program. PIC results, however, are given in Table E-9 and will continue to be Non-ODCM surveillance to satisfy our commitment to the surrounding community.
The results were compared with that generated during the previous ISFSI pre-operational periods (Ref. 11) and the current and previous CCNPP REMP periods. These comparisons show little deviations from these periods and are very close to the natural background levels for the region with the exception of TLDs around the north end of the ISFSI. More detailed discussions of these results are given in Section III. C.III.B. PROGRAM III.B.1 Obieectives The objectives of the radiological environmental monitoring program for the ISFSI are: a. To satisfy the community concern regarding the impact of the ISFSI on the environment, b. To verify, that radioactivity and ambient radiation levels attributable to operation of the ISFSI are within the limits specified in the Environmental Radiation Protection Standards as stated in 40 CFR Part 190, 21 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8
- c. To detect any measurable buildup of long-lived radionuclides in the environment due to the ISFSI, d. To monitor and evaluate ambient radiation levels around the ISFSI, e. To determine whether any statistically significant increase occurs in the con-centration of radionuclides near the ISFSI.III.B.2 Sample Collection The locations of the individual sampling sites are listed in Table A-2 and shown in Figures A-4 and A-5. All samples were collected by contractors to, or personnel of, Constellation Energy personnel according to Constellation Energy Laboratory Procedures (Ref. 7).III.B.3 -Data Interpretation Many results in environmental monitoring occur at or below the minimum detectable activity (MDA). In this report, all results at or below the relevant MDA are reported as being "less than" the MDA value.III.B.4 Program Exceptions There were no program exceptions during this operating period III.C. RESULTS AND DISCUSSIONS All the environmental samples collected were analyzed using Constellation Energy laboratory procedures (Ref. 8). The analytical results for this reporting period are presented in Appendix B and are also summarized for the period in Table 4. For discussion, the analytical results are divided into three categories.
The categories are the Atmospheric Environment, the Terrestrial Environment, and Direct Radiation.
These categories are further divided into subcategories according to sample type (e.g., Vegetation and Soil for Terrestrial Environment).
III.C.1 Atmospheric Environment The atmospheric environment was monitored by analyzing air particulate filters. These samples were collected from five locations surrounding the ISFSI.No source of airborne radioiodine exists for the ISFSI. Airborne radioiodine is, therefore, not considered in assessing the radiological impact of the ISFSI.III.C. L.a Air Particulate Filters Weekly composite air particulate filter samples were collected from five locations during the period. These locations are On Site before the Entrance to Camp Conoy (sample code Al; in common with the CCNPP REMP), Meteorological Station (SFA 1), CCNPP Visitor's Center 22 January I -December 31, 2006 Docket Nos. 50-317/50-318/72-8 (SFA2), NNW of the ISFSI (SFA3), and SSE of the ISFSI (SFA4). These samples were an-alyzed for beta radioactivity and gamma emitting radionuclides.
Weekly analyses for beta activity on air particulate filters collected from all five locations showed values characteristic of levels routinely observed in the REMP .These values ranged from 0.7 x 10-2 to 4.5 x 10-2 pCi/m 3 for the'indicator locations and 0.7 x 10-2 to 3.3 x 10-2 pCi/m 3 for the control location.
The location with the highest overall mean of: 2.3 x 10-2 pCi/m 3 was SFA4, SSE of ISFSI.Gamma spectrometric analyses of monthly composited air particulate samples exhibited no detectable concentrations of any plant-related radionuclides in any of these samples. Naturally occurring radionuclides, such as Be-7, were detected in nearly all samples.III.C.2 Terrestrial Environment The terrestrial environment was monitored by analyzing samples of vegetation and soil collected quarterly from the vicinity of the air sampling locations for the ISFSI., III.C.2.a Veaetation Vegetation samples were collected quarterly from five locations during the year. These.locations are: Meteorological Station (sample code SFbl), CCNPP Visitor's Center (sample code SFb2), NNWof the ISFSI (sample code SFb3), SSE of the ISFSI (sample code SFb4), and On Site before the Entrance .to Camp Conoy (sample code SFb5). These samples were analyzed for gamma emitters.No detectable concentration of plant-related radionuclides were found in any of these samples.Naturally occurring radionuclides such as K-40 were detected in all samples.III.C.2.b Soils Soil samples were collected quarterly from five locations surrounding the ISFSI in the vicinity of the air-samplers.
These locations are: Meteorological Station (sample code SFS1),-CCNPP Visitor's Center (sample code SFS2), NNW of the ISFSI (sample code SFS3); SSE of the ISFSI (sample code SFS4), and On Site before the Entrance to Camp Conoy (sample code SFS5).Soil samples were analyzed for gamma.emitting radionuclides.
Cesium-137 was detected in thirteen quarterly samples from both indicator and control locations.
The Cs-137 concentrations ranged from 37 + 45 to 922 +/- 127 pCi/kg. While the presence of Cs-137in these samples may be plant-related, this range is consistent with that found to be due to the residual fallout from past atmospheric nuclear weapons. testing. The activities of this radionuclide are well below the federal limits established in 40 CFR Part 190, "Environmental Radiation Protection Standards for Nuclear Power Operations" and are comparable to those observed in previous annual reporting periods for the CCNPP REMP and in the earlier pre-operational data for the ISFSI.No other detectable concentrations of plant-related radionuclides were found in any of these samples. Naturally occurring radionuclides such as K-40, were also detected in all these samples.'23 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 III.C.3 Direct Radiation Direct radiation is measured by a network of TLDs surrounding the ISFSI. These TLDs are collected quarterly from nineteen locations surrounding the ISFSI, plus one control TLD location at the Visitor's Center (sample code SFDR7). The locations include On Site before the Entrance to Camp Conoy (sample code DR7, common to both the CCNPP Program and the ISFSI Program) and the Meteorological Station (sample code DR30, previously a location maintained for historical continuity.)
The other sampling locations are: SW of ISFSI, (sample code SFDR1); NNW of ISFSI, (sample code SFDR2); North of ISFSI, (sample code SFDR3); NE of ISFSI, (sample code SFDR4); East of ISFSI, (sample code SFDR5); ESE of ISFSI, (sample code SFDR6); NNW of ISFSI, (sample code SFDR8); SSE of ISFSI, (sample code SFDR9); NW of ISFSI, (sample code SFDR1O); WNW of ISFSI, (sample code SFDR1 1); WSW of ISFSI, (sample code SFDR12); South of ISFSI, (sample code SFDR1!3);
SE of ISFSI, (sample code SFDR14); ENE of ISFSI, (sample code SFDR15); SSW of ISFSI, (sample code SFDR16); NNE of ISFSI, (sample code SFDR17) and West of ISFSI, (sample code SFDR18). Sampling locations are shown on Figures A-4 and A-5.The mean 90 day ambient radiation measured at the ISFSI indicator locations was 26.79 mR and ranged from 9.53 to 42.06 mR as reported in Table 4. The control location showed a 90 day mean of 12.64 mR and ranged from 12.11 to 13.45 mR. The location with the highest overall mean of 39.40 mR with a range of 37.46 to 42.06 mR was SFDR18, West of ISFSI. These readings are consistent with those expected from the storage of spent fuel in the ISFSI. A comparison of the average monthly radiation levels per calendar year of the ISFSI TLD data from the indicator locations with the ISFSI control location at the Visitor's Center, SFDR7, can be seen in Figure 7.III.D. CONCLUSION Low levels of Cs-137 were observed in the environment surrounding the ISFSI during the period. The Cs- 137 observations were attributed to fallout from past atmospheric weapons testing. No other plant-related radionuclide was observed in the environs of the ISFSI.In general, the results in the following tables continue the historical trends previously observed at the official sites of the CCNPP REMP.24 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 FIGURE 7 Mean TLD Gamma Dose, ISFSI 10 9 7 --*- Control Location (SFDR7)--- ISFSI Mean (DR7 & 30, SFDR1-6, 8-18)U,)CU-0 0 CO E 6-5-4-3 2 0 90 91 92 93 94 95 96 97 98 99 00 01 02 03 04 05 06 25 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table 3 Synopsis of 2006 Calvert Cliffs Nuclear Power Plant Independent Spent Fuel Storage Installation Radiological Environmental Monitoring Program Sample Type Sampling Frequency Number of Locations Number Collected Analysis Analysis Frequency 1 Number Analyzed Atmospheric Environment Air Particulates 2 Direct Radiation Ambient Radiation Terrestrial Environment Vegetation Soil W 5 258 Gross Beta W 258 Gamma MC 60 Q 20 480 TLD Q 480 Q Q 5 5 20 20 Gamma Gamma Q Q 20 20'W-weekly, M=monthly, Q=quarterly, SA=semiannual, A=annual, C=composite 2 Beta counting is performed after >72 hour decay, Gamma spectroscopy performed on monthly composites of weekly samples 26 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE 4 Annual Summary of Radioactivity in the Environs of the Calvert Cliffs Nuclear Power Plant Independent Spent Fuel Storage Installation Medium or Pathway Sampled (Unit of Measurement)
Type and Total Number of Analyses Performed Lower Limit of Detection (LLD)Indicator Locations Mean (F)/Range'.
Location with Highest Annual Mean Name/Distance
& Direction 2 Highest Annual Mean (F) /Range1 Control Locations Mean (F)/Rangel Atmospheric Environment Air Particulates (10-2 pCi/m 3)Direct Radiation Ambient Radiation (mR/90 days)Gross Beta (258)0.5 1.9 (206/206)(0.7-4.5)SSE of ISFSI SFA4 0.1 km SSE 2.3 (52/52)(0.9-4.5)1.7 (52/52)(0.7-3.3)TLD (480)26.79 (456/456)(9.53-42.06)
West of ISFSI SFDR18 0.1 kmW 39.40 (24/24)(37.46-42.06) 12.64 (24/24)(12.11-13.45)
Terrestrial Environment Soil Gamma (20) 17 345 (10/16) NNW of ISFSI 626 (4/4)(pCi/kg) Cs-137 (37-922) SFS3 (221-922)0.1 kmNNW 1 Mean and range based upon detectable measurements only. Fraction (F) of detectable measurement at specified locations is indicated in parentheses 2 From the centerpoint of the ISFSI facility 106 (3/4)(65-1-78)27 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 IV. REFERENCES (1) Cohen, L. K., "Preoperational Environmental Radioactivity Monitoring Program at Calvert Cliffs Units 1 and 2", NUS No. 882 Semiannual Report January-June 1971, December 1971; NUS No.1025 Annual Report 1971, March 1973.(2) Cohen, L. K., "Preoperational Environmental Radioactivity Monitoring Program at Calvert Cliffs Units 1 and 2", NUSNo. 1137 Annual Report 1972, December 1973.(3) Cohen, L. K. and Malmberg, M.S., "Preoperational Environmental Radioactivity Monitoring Program at Calvert Cliffs Units 1 and 2", NUS No. 1188, Annual Report 1973, October 1974.(4) Malmberg, M. S., "Preoperational Environmental Radioactivity Monitoring Program at Calvert Cliffs Units 1 and 2", NUS No. 1333, Data Summary Report, September 1970 to September 1974, July 1975 (5) Calvert Cliffs Nuclear Power Plant, Units 1 and 2, License Nos. DPR-53 and DPR-69, Technical Specification 5.6.2; Annual Radiological Environmental Operating Report.(6) Offsite Dose Calculation Manual for the Calvert Cliffs Nuclear Power Plant.(7) CP-234, Specification and Surveillance for the Radiological Environmental MonitoringProgram.
(8) Constellation Energy Laboratory Procedures Manual, General Services Department.
(9) Constellation Energy, "Land Use Survey Around Calvert Cliffs Nuclear Power Plant, August 2006." (10) Calvert Cliffs Independent Spent Fuel Storage Installation Technical Specifications, Appendix A to Materials License SNM-2505 (11) Baltimore Gas and Electric Company, Radiological Environmental Monitoring Program Pre-Operational Report for the Calvert Cliffs Independent Spent Fuel Storage Installation, August 1990 -November 1993, February 1994.(12) CP-501, Liquid and Steam Sampling Techniques 28 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 APPENDIX A Sample Locations for the REMP and the ISFSI Appendix A contains information concerning the environmental samples which were collected during this operating period.Sample locations and specific information about individual locations for the CCNPP REMP are given in Table A-1. Figure A-I shows the location of the CCNPP in relation to Southern Maryland and the Chesapeake Bay. Figures A-2 and A-3 show the locations of the power plant sampling sites in relation to the plant site at different degrees of detail.Sample locations and specific information about individual locations for the ISFSI radiological environmental monitoring program are given in Table A-2. Figures A-4 and A-5 show the locations of the ISFSI sampling sites in relation to the plant site at different degrees of detail.29 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK)30 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE OF CONTENTS -SAMPLING LOCATIONS Table Title Page A-i Locations of Environmental Sampling Stations for the Calvert Cliffs Nuclear Power Plant..33 A-2 Locations of Environmental Sampling Stations for the Independent Spent Fuel Storage Installation at Calvert C liffs ................................................................................................
41 Figure Title Page A-i Map of Southern Maryland and Chesapeake Bay Showing Location of Calvert Cliffs N uclear Pow er Plant .............................................................................................................
35 A-2 Calvert Cliffs Nuclear Power Plant Sampling Locations, 0-2 Miles ..................................
37 A-3 Calvert Cliffs Nuclear Power Plant Sampling Locations, 0-10 Miles ................................
39 A-4 Independent Spent Fuel Storage Installation Sampling Locations
.....................................
42 A-5 Enlarged Map of the Independent Spent Fuel Storage Installation Sampling Locations
........ 43 31 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK)32 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE A-1 Locations of Environmental Sampling Stations for the Calvert Cliffs Nuclear Power Plant Distance' Direction!-
Station Description (KM) (Miles) (Sector)Al On Site before Entrance to Camp Conoy 0.7 0.4 S A2 Camp Conoy at Emergency Siren 2.5 1.6 SSE A3 Bay Breeze Road 2.6 1.6 SE A4 Route 765 Lusby 2.9 1.8 SSW A5 Emergency Operations Facility (EOF) 19.3 12.0 WNW DRI On Site along Cliffs 0.6 0.4 NW DR2 Route 765, Auto Dump 2.7 1.7 WNW DR3 Route 765,Giovanni's Tavern (Knotty Pine) 2.3 1.4 W DR4 Route 765, across from White Sands Drive 2.0 1.2 WSW DR5 Route 765, John's Creek 2.4 1.5 SW DR6 Route 765 Lusby 2.9 1.8 SSW DR7 2 On Site before Entrance to Camp Conoy 0.7 0.4 S DR8 Camp Conoy at Emergency Siren 2.5 1.6 SSE DR9 Bay Breeze Road 2.6 1.6 SE DR1O Calvert Beach Rd. and Decatur Street 6.4 4.0 NW DR 1I Dirt road off Mackall & Parran Roads 6.6 4.1 WNW DR12 Mackall and Bowen Roads 6.7 4.2 W DR13 Mackall Rd. near Wallville 6.1 3.8 WSW DR14 Rodney Point 6.4 4.0 SW DR15 Mill Bridge and Turner Roads 6.2 3.9 SSW DR16 Across from Appeal School 6.5 4.0 S DR17 Cove Point and Little Cove Point Roads 5.9 3.7 SSE DRI 8 Cove Point 7.1 4.4 SE DR19 Long Beach 4.4 2.7 NW DR20 On Site near shore 0.4 0.2 NNW DR21 Emergency Operations Facility, (EOF) 19.3 12.0 WNW DR22 Solomons Island 12.5 7.8 S DR23 Taylors Island, Carpenter's Property 12.6 7.8 ENE Ial,2 Discharge Area 0.3 0.2 N Ia3 Camp Conoy 0.9 0.6 E Ia4,5 Patuxent River N/A N/A N/A Ia6 Kenwood Beach 10.7 6.6 NNW Ial0 Hog Island 15.3 9.5 SSE Lbl,2,3 Garden Off Bay Breeze Road 2.6 1.6 SSE Ib4,5,6 On Site before Entrance to Camp Conoy 0.7 0.4 S Ib7,8,9 Emergency Operations Facility (EOF) 19.3 12.0 WNW Wal Intake Area 0.2 0.1 NNE Wa2 Discharge Area 0.3 0.2 N Wbl Shoreline at Barge Rd. 0.6 0.4 ESE Distance and direction from the central point between the two containment buildings.
2 Common to both the REMP and ISFSI monitoring program 33 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK)34 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 FIGURE A-1 Map of Southern Maryland and Chesapeake Bay Showing Location of Calvert Cliffs Nuclear Power Plant 35 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK)36 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 FIGURE A-2 Calvert Cliffs Nuclear Power Plant Sampling Locations 0-2 Miles 37 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK)38 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 FIGURE A-3 Calvert Cliffs Nuclear Power Plant Sampling Locations 0-10 Miles 39 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK)40 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE A-2 Locations of Environmental Sampling Stations for the Independent Spent Fuel Storage Installation at Calvert Cliffs Distance' Direction' Station Description (KM) (Sector)Air Particulate A1 2 On Site before Entrance to Camp Conoy 0.3 ESE SFA1 Meteorological Station 0.3 NW SFA2 CCNPP Visitor's Center 0.8 N SFA3 NNW of ISFSI 0.1 NNW SFA4 SSE ofISFSI 0.1 SSE Direct Radiation SFDR1 SW of ISFSI 0.2 SW SFDR2 NNW of ISFSI 0.2 NNW SFDR3 North of ISFSI 0.1 N SFDR4 NE of ISFSI 0.1 NE SFDR5 East of ISFSI 0.1 E SFDR6 ESE of ISFSI 0.1 ESE.SFDR7 CCNPP Visitor's Center 0.8 N SFDR8 NNW of ISFSI 0.1 NNW SFDR9 SSE of ISFSI 0.1 SSE SFDR1O NW of ISFSI 0.1 NW SFDR11 WNW of ISFSI 0.1 WNW SFDR12 WSW of ISFSI 0.04 WSW SFDR13 South ofISFSI 0.1 S SFDR14 SE of ISFSI 0.1 SE SFDR15 ENE of ISFSI 0.1 ENE SFDR16 SSW of ISFSI 0.04 SSW SFDRI7 NNE ofISFSI 0.1. NNE SFDR18 West of ISFSI 0.04 W DR7 2 On Site before Entrance to Camp Conoy 0.3 ESE DR30 Meteorological Station 0.3 NW Vegetation
"_*_, SFbl Meteorological Station 0.3 NW SFb2 CCNPP Visitor's Center 0.8 N SFb3 NNW of ISFSI 0.1 NNW SFb4 SSE of ISFSI 0.1 SSE SFb5 On Site before Entrance to Camp Conoy 0.3 ESE Soil _SFS1 Meteorological Station 0.3 NW SFS2 CCNPP Visitor's Center 0.8 N SFS3 NNW of ISFSI 0.1 NNW SFS4 SSE of ISFSI 0.1 SSE SFS5 On Site before Entrance to Camp Conoy 0.3 ESE'Distance and direction from the central point of the ISFSI 2 Common to both REMP and ISFSI monitoring program 41 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 FIGURE A-4 Independent Spent Fuel Storage Installation Sampling Locations 42 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 FIGURE A-5 Enlarged Map of the Independent Spent Fuel Storage Installation Sampling Locations 43 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK)44 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 APPENDIX B Analysis Results for the REMP and the ISFSI Appendix B is a presentation of the analytical results for the CCNPP and the ISFSI radiological environmental monitoring programs.45 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK)46 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE OF CONTENTS -ANALYTICAL RESULTS Table Title Page B-1 Concentration of Tritium and Gamma Emitters in Bay Water ..........................................
49 B-2 Concentration of Gamma Emitters in the Flesh of Edible Fish ..........................................
50 B-3 Concentration of Gamma Emitters in Oyster Samples ......................................................
51 B-4 Concentration of Gamma Emitters in Shoreline Sediment .................................................
52 B-5 Concentration of Iodine-131 in Filtered Air .......................................................................
53 B-6 Concentration of Beta Emitters in Air Particulates
............................................................
55 B-7 Concentration of Gamma Emitters in Air Particulates
.....................................................
59 B-8a Concentration of Gamma Emitters in Vegetation Samples ................................................
60 B-8b Concentration of Gamma Emitters in Vegetation From Locations Around the IFSFI ..... 61 B-9 Concentration of Gamma Emitters in Soil Samples From Locations Around the ISFSI ........ 62 B-10 Typical MDA Ranges for Gamma Spectromietry
..............................................................
63 B-1I Typical LLDs for Gamma Spectrometry
...........................................................................
64 B -12 D irect R adiation .......................................................................................................................
65 47 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK)48 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table B-1 Concentration of Tritium and Gamma Emitters in Bay Water (Results in units of pCi/L +/- 2o')Sample Code Sample Date H-3 1 Gamma Emitters Wal Intake Vicinity Wa2 Discharge Vicinity 1/31/2006 2/28/2006 3/31/2006 4/28/2006 5/31/2006 6/29/2006 6/30/2006 7/31/2006 8/31/2006 9/29/2006 10/31/2006 11/30/2006 12/28/2006 1/31/2006 2/28/2006 3/31/2006 4/28/2006 5/31/2006 6/29/2006 6/30/2006 7/31/2006 8/31/2006 9/29/2006 10/31/2006 11/30/2006 12/28/2006
<446<456<340<340<457<457<340<340********1 Quarterly composites of monthly samples* All Non-Natural Gamma Emitters <MDA 49 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table B-2 Concentration of Gamma Emitters in the Flesh of Edible Fish (Results in units of pCi/kg (wet) +/- 2c)Sample Sample Type Gamme Date SAMPLE CODE Emitters lal 8/22/2006 Bluefish Discharge Area la2 8/22/2006 Spanish Mackeral 'Discharge Area la4 1 8/22/2006 Bluefish Patuxent River la5 1 8/22/2006 Spanish Mackeral Patuxent River Control Location All Non-Natural Gamma Emitters <MDA i 50 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table B-3 Concentration of Gamma Emitters in Oyster Samples (Results in units of pCi/kg (wet) +/- 2a)SAMPLE CODE Sample Date Gamma Emitters la3 3/24/2006
- Camp Conoy 6/19/2006
- 8/22/2006
- 10/26/2006
- la6 1 3/24/2006
- Kenwood Beach 6/19/2006
- 8/22/2006
- 10/26/2006
- 1 Control Location All Non-Natural Gamma Emitters <MDA 51 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table B-4 Concentration of Gamma Emitters in Shoreline Sediment (Results in units of pCi/kg (dry) +/- 2a)SAMPLE CODE Sample Date Gamma Emitters Wbl 6/26/2006
- Shoreline at Barge Rd. 11/20/2006
- All Non-Natural Gamma Emitters <MDA 52 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table B-5 Concentration of Iodine-131 in Filtered Air (Results in units of 10 3 pCi/M 3+/- 2a)Start Date Stop Date Al Entrance to Camp Conoy A2-Camp Conoy Siren A3 Bay Breeze Rd A4 Route 765 at Lusby A5 1 EOF 1/2/2006 1/9/2006 1/16/2006 1/23/2006 1/30/2006 2/6/2006 2/13/2006 2/20/2006 2/27/2006 3/6/2006 3/13/2006 3/20/2006 3/27/2006 4/3/2006 4/10/2006 4/17/2006 4/24/2006 5/1/2006 5/8/2006 5/15/2006 5/22/2006 5/29/2006 6/5/2006, 6/12/2006 6/19/2006 6/26/2006 7/3/2006 7/10/2006 7/17/2006 7/24/2006 7/31/2006 8/7/2006 8/14/2006 8/21/2006 1/9/2006 1/16/2006 1/23/2006 1/30/2006 2/6/2006 2/13/2006 2/20/2006 2/27/2006 3/6/2006 3/13/2006 3/20/2006 3/27/2006 4/3/2006 4/10/2006 4/17/2006 4/24/2006 5/1/2006 5/8/2006 5/15/2006 5/22/2006 5/29/2006 6/5/2006 6/12/2006 6/19/2006 6/26/2006 7/3/2006 7/10/2006 7/17/2006 7/24/2006 7/31/2006 8/7/2006 8/14/2006 8/21/2006 8/28/2006*******************************************t"**A"*1 Control Location 2 Sampler Malfunction; Loss of Data 3 Operator Error; Loss of Data" All Non-Natural Gamma Emitters <MDA 53 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table B-5 -Continued Concentration of Iodine-131 in Filtered Air (Results in units of 10-3 pCi/m 3+/- 2cr)Start Date Stop Date Al Entrance to Camp Conoy A2 Camp Conoy Siren A3 Bay Breeze Rd A4 Route 765 at Lusby A5 1 EOF 8/28/2006 9/4/2006 9/11/2006 9/18/2006 9/25/2006 10/2/2006 10/9/2006 10/16/2006 10/23/2006 10/30/2006 11/6/2006 11/13/2006 11/20/2006 11/27/2006 12/5/2006 12/12/2006 12/18/2006 12/25/2006 9/4/2006 9/11/2006 9/18/2006 9/25/2006 10/2/2006 10/9/2006 10/16/2006 10/23/2006 10/30/2006 11/6/2006 11/13/2006 11/20/2006 11/27/2006 12/4/2006 12/11/2006 12/18/2006 12/25/2006 1/1/2007*A"k***********"*******************1 Control Location 54 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table B-6 Concentration of Beta Emitters in Air Particulates (Results in units of 10-2 pCi/m 3+/- 2cr)Start Date Stop Date Al Entrance to Camp Conoy A2 Camp Conoy Siren A3, Bay Breeze Rd, A4 Route 765 at Lusby A5 1 EOF 1/2/2006 1/9/2006 1/16/2006 1/23/2006 1/30/2006 2/6/2006 2/13/2006 2/20/2006 2/27/2006 3/6/2006 3/13/2006 3/20/2006 3/27/2006 4/3/2006 4/10/2006 4/17/2006 4/24/2006 5/1/2006 5/8/2006 5/15/2006 5/22/2006 5/29/2006 6/5/2006 6/12/2006 6/19/2006 6/26/2006 7/3/2006 7/10/2006 7/17/2006 7/24/2006 7/31/2006 8/7/2006 8/14/2006 8/21/2006 1/9/2006 1/16/2006 1/23/2006 1/30/2006 2/6/2006 2/13/2006 2/20/2006 2/27/2006 3/6/2006 3/13/2006 3/20/2006 3/27/2006 4/3/2006 4/10/2006, 4/17/2006 4/24/2006 5/1/2006 5/8/2006 5/15/2006 5/22/2006 5/29/2006 6/5/2006 6/12/2006 6/19/2006 6/26/2006 7/3/2006 7/10/2006 7/17/2006 7/24/2006 7/31/2006 8/7/2006 8/14/2006 8/21/2006 8/28/2006 1.7 +/- 0.2 1.9+/-0.3 1.3 +/- 0.2 1.7 +/- 0.2 1.5 +/- 0.2 1.9 +/- 0.3 3.0 +/- 0.3.3.1 +/-0.3 2.3 +A 0.3 2.8 +/- 0.3 3.0 +/- 0.3 1.4 +/- 0.3 2.3 +/- 0.2 1.9 +/- 0.3 2.1 +/-0.3 1.1 +/-0.2 1.5 +/- 0.2 1.5 +/- 0.2 1.2 +/- 0.2 1.0 +/- 0.2 1.6 +/- 0.2 1.5 +/- 0.2 1.1 +/-0.2 1.4 +/-0.2 1.1 +/-0.2 1.3 +/- 0.2 1.8 +/- 0.2 1.6 +/- 0.2 1.3 +/- 0.2 2.1 +/-0.2 1.8 +/- 0.2 1.7 +/- 0.2 1.9 +/- 0.2 2.3 +/- 0.2 1.5 +/- 0.2 1.4 +/- 0.2 1.3 +/- 0.2 1.3 +/- 0.2 1.2 +/- 0.2 1.6 +/- 0.2 2.4 +/- 0.2 2.2 +/- 0.2 1.9 +/- 0.2 1.8 +/- 0.2 2.0 +/- 0.2 1.4 +/- 0.2 2.1 +/-0.2 1.8 +/- 0.2 1.4 +/- 0.2 1.2 +/- 0.2 1.6 +/- 0.2 1.4 +/- 0.2 0.9 +/- 0.2 1.2 +/-0.2 1.5 +/- 0.2 1.8 +/-0.2 1.0 +/-0.2 1.4 +/-0.2 0.8 +/- 0.2 1.1 +/-0.2 1.4 +/- 0.2 1.2 +/- 0.2 1.3 +/- 0.2 1.9 +/- 0.2 2.4 +/- 0.3 1.8 +/- 0.2 2.0 +/- 0.2 2.8 +/- 0.2 1.1 +/-0.2 1.4 +/- 0.2 1.1 +/-0.2 1.3 +/- 0.2 1.3 +/- 0.2 1.6 +/- 0.2 2.0+/-0.2 2.2+/-0.2 1.5 +/- 0.2 1.7 +/- 0.2 2.2 +/- 0.2 1.1 +/-0.2 1.9 +/-0.2 1.4 +/- 0.2 1.5 +/- 0.2 0.9 +/- 0.2 2 2 1.0 +/- 0.2 1.1 +/-0.2 1.4 +/- 0.2 1.9 +/- 0.3 1.1 +/-0.2 1.1 +/-0.2 0.8 +/- 0.2 1.6 +/- 0.2 1.5 +/- 0.2 1.0 +/- 0.2 2.3 +/- 0.2 1.8 +/- 0.2 2.6+/-0.3 1.7 +/- 0.2 1.8 +/- 0.2 2.6+/-0.3 1.7 +/- 0.2 2.0 +/-.0.3 1.8 +/- 0.3 1.5 +/- 0.2 2.1 +/-0.3 1.8 +/- 0.3 0.9 +/- 0.2 2.8 +/- 0.3 2.3 +/- 0.3 2.5+/- 0 3 2.5 +/- 0.2 1.2 +/-0.2 2.3 +/- 0.2 1.5 +/- 0.2 1.5 +/- 0.2 1.0 +/- 0.2 1.3 +/- 0.2 1.3 +/- 0.2 1.0 +/- 0.2 1.0 +/- 0.2 1.3 +/- 0.2 1.4 +/- 0.2 1.0 +/- 0.2 1.6 +/-0.2 1.2 +/-0.2 1.5 +/-0.2 1.6 +/-0.2 1.7 +/- 0.2 0.9 +/- 0.2 2.2 +/- 0.2 2.1 +/-0.2 1.9 +/- 0.2 2.0 +/- 0.2 2.9 +/- 0.2 1.5 +/- 0.2 1.6 +/- 0.2 1.2 +/- 0.2 1.7 +/- 0.2 1.2 +/- 0.2 1.8 +/- 0.2 2.6+/-0.2 2.6 +/- 0.2 2.3+/-0.3 2.4+/-0.2 2.4 +/- 0.2 1.2 +/- 0.2 2.0 +/- 0.2 1.9 +/- 0.2 1.9 +/- 0.2 1.2 +/- 0.2 1.9 +/- 0.3 1.5 +/- 0.2 1.1 +/-0.2 1.4 +/- 0.2 1.8 +/- 0.2 2.0 +/- 0.2 1.5 +/- 0.2 2.2 +A 0.2 1.1 +/-0.2 2.5+/-0.3 2.6 +/- 0.3 2.0 +/- 0.3 2.1 +/-0.3 3.0 +/- 0.3 2.7 +/- 0.3 2.5 +/- 0.3 3.1 +/-0.3 4.0 +/- 0.3' Control Location 2 Sampler Malfunction; Loss of Data 55 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table B-6 -Continued Concentration of Beta Emitters in Air Particulates (Results in units of 10-2 pCi/m 3+/- 2cr)Start Date Stop Date Al Entrance to Camp Conoy A2 Camp Conoy Siren A3 Bay Breeze Rd A4 Route 765 at Lusby A5 1 EOF 8/28/2006 9/4/2006 9/11/2006 9/18/2006 9/25/2006 10/2/2006 10/9/2006 10/16/2006 10/23/2006 10/30/2006 11/6/2006 11/13/2006 11/20/2006 11/27/2006 12/4/2006 12/12/2006 12/18/2006 12/25/2006 9/4/2006 9/11/2006 9/18/2006 9/25/2006 10/2/2006 10/9/2006 10/16/2006 10/23/2006 10/30/2006 11/6/2006 11/13/2006 11/20/2006 11/27/2006 12/4/2006 12/11/2006 12/18/2006 12/25/2006 1/1/2007 1.3 +/- 0.2 2.2+/-0.2 1.2 +/- 0.2 1.5 +/- 0.2 1.7 +/- 0.2 1.6 +/- 0.2 2.2 +/- 0.2 1.3 +/- 0.2 1.3 +/- 0.2 2.3+/-0.2 1.5 +/-0.2 1.4 +/- 0.2 1.7 +/- 0.2 1.4 +/- 0.2 2.8 +/- 0.2 3.4+/-0.2 1.6 +/- 0.2 1.9 +/- 0.2 1.0 +/- 0.2 1.9 +/- 0.2 1.0 +/- 0.2 1.4 +/- 0.2 1.5 +/- 0.2 1.8 +/-0.2 2.3+/-0.2 1.7 +/- 0.2 1.7 +/- 0.2 3.0 +/- 0.3, 1.8 +/-0.2 1.6 +/-0.2 1.6 +/-0.2 1.9 +/-0.2 2.9 +/- 0.2 3.9+/-0.2 1.9 +/- 0.2 2.0 +/- 0.2 1.0 +/- 0.2 2.0+/-0.2 1.0 +/- 0.2 1.6 +/- 0.2 1.9 +/- 0.3 1.6 +/- 0.3 3.0 +/- 0.3 1.8 +/- 0.3 2.5 +/- 0.3 3.9 +/- 0.4 1.2 +/- 0.2 1.5 +/- 0.2 1.5 +/- 0.2 1.8 +/- 0.2 2.8 +/- 0.2 4.4 +/- 0.3 1.8 +/- 0.2 1.7 +/- 0.2 0.9 +/- 0.2 2.0+/-0.2 0.9 +/- 0.2 1.5 +/- 0.2 1.6 +/-0.2 1.5 +/- 012 2.5 +/- 0.2 1.2 +/- 0.2 1.5 +/- 0.2 2.5 +/- 0.2 1.5 +/- 0.2 1.6 +/- 0.2 1.8 +/- 0.2 2.0 +/- 0.2 2.8+/-0.2 3.5 +/-0.2 2.4 +/- 0.2 2.0 +/- 0.2 1.1 +/-0.2 2.8 +/- 0.3 1.0 +/- 0.2 2.5+/-0.3 2.3 +/- 0.3 2.1 +/-0.3 3.1 +/-0.3 2.0 +/- 0.3 1.7 +/- 0.2 3.9 +/- 0.4 1.2+/- 0.1 1.2 +/- 0.2 1.5 +/- 0.2 1.9 +/- 0.2 2.5 +/- 0.2 3.8+/-0.2 1.8 +/- 0.2 1.9 +/- 0.2 1 Control Location 56 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table B-6 -Continued Concentration of Beta Emitters in Air Particulates (Results in units of 102 pCi/M 3+/- 2c)Start Date Stop Date SFA1 MET Station SFA2 1 Visitors Center SFA3 NNW of ISFSI SFA4 SSE of ISFSI 1/2/2006 1/9/2006 1/16/2006 1/23/2006 1/30/2006 2/6/2006 2/13/2006 2/20/2006 2/27/2006 3/6/2006 3/13/2006 3/20/2006 3/27/2006 4/3/2006 4/10/2006 4/17/2006 4/24/2006 5/1/2006 5/8/2006 5/15/2006 5/22/2006 5/29/2006 6/5/2006 6/12/2006 6/19/2006 6/26/2006 7/3/2006 7/10/2006 7/17/2006 7/24/2006 7/31/2006 8/7/2006 8/14/2006 8/21/2006 1/9/2006 1/16/2006 1/23/2006 1/30/2006 2/6/2006 2/13/2006 2/20/2006 2/27/2006 3/6/2006 3/13/2006 3/20/2006 3/27/2006 4/3/2006 4/10/2006 4/17/2006 4/24/2006 5/1/2006 5/8/2006 5/15/2006 5/22/2006 5/29/2006 6/5/2006 6/12/2006 6/19/2006 6/26/2006 7/3/2006 7/10/2006 7/17/2006 7/24/2006 7/31/2006 8/7/2006 8/14/2006 8/21/2006 8/28/2006 1.6 +/-0.3 1.6 +/- 0.2 1.2 +/- 0.2 1.7 +/- 0.2 1.3 +/- 0.2 1.7 +/- 0.2 1.5 +/-0.2 2.6+/-0.3 2.1 +/-0.2 2.3+/-0.2 2.7 +/- 0.3 0.9 +/- 0.2 2.6+/-0.3 1.9 +/-0.2 1.6 +/- 0.2 1.2 +/- 0.2 1.5 +/- 0.2 1.5 +/- 0.2 0.9+/-0.2 1.2 +/- 0.2 1.6 +/- 0.2 1.8 +/- 0.2 1.0 +/- 0.2 1.6 +/-0.2 1.2 +/- 0.2 1.6 +/- 0.2 1.7 +/- 0.2 1.6 ÷1- 0.2 1.6 +/- 0.2 2.3 +/- 0.2 1.6 +/-0.2 1.7 +/- 0.2 1.9 +/- 0.2 2.6 +/- 0.2 1.4 +/- 0.2 1.7 +/- 0.2 1.3 +/- 0.2 1.5 +/- 0.2 1.4 +/- 0.2 1.5 +/- 0.2 2.3+/-0.2 2.3 +/- 0.2 2.0 +/- 0.2 2.0+/-0.2 2.1 +/-0.2 1.3 +/- 0.2 1.8 +/- 0.2 1.4 +/- 0.2 1.3 +/- 0.2 1.1 +/-0.2 1.4 +/- 0.2 1.3+/- 0.2 0.8+/-0.2 1.1 +/-0.2 1.5 +/- 0.2 1.7 +/- 0.2 1.1 +/-0.2 1.7 +/- 0.2 0.9+/-0.2 1.5 +/- 0.2 1.6 +/- 0.2 1.7 +/- 0.2 1.5 +/-0.2 2.4 +/- 0.2 2.4 +/- 0.2 2.0+/-0.2 1.9 +/- 0.2 2.5 +/- 0.2 2 1.3 +/- 0.2 2 1.7 +/- 0.3 1.1 +/-0.2 1.6 +/- 0.2 2.4 +/- 0.2 2.2+/-0.2 1.9 +/-0.2 1.9 +/-0.2 2.3 +/- 0.2 1.1 +/-0.2 2.0 +/- 0.2 1.5 +/- 0.2 1.3 +/- 0.2 1.0 +/- 0.2 1.5 +/-0.2 1.6 +/- 0.2 0.7 +/- 0.1 1.0 +/- 0.2 1.3 +/- 0.2 1.2 +/- 0.2 1.1 +/-0.2 1.2 +/- 0.2 0.8 +/- 0.2 1.7 +/- 0.2 1.6 +/- 0.2 1.9 +/-0.2 1.7 +/-0.2 2.4 +/- 0.2 2.3 +/- 0.2 2.0 +/- 0.2 2.2 +/- 0.2 2.6 +/- 0.2 1.5 +/- 0.2 2.2 +/- 0.2 1.5 +/- 0.2 1.9 +/- 0.2 1.9 +/- 0.2 1.4 +/- 0.2 3.0+/-0.3 2.9 +/-,0.3 3.0 +/- 0.3 2.7+/-0.3 3.2 +/- 0.3 0.9+/-0.2 2.5 +/- 0.2 2.1 +/-0.3 1.8 +/- 0.2 1.2 +/- 0.2 1.8 +/- 0.2 1.8 +/- 0.2 1.7 +/- 0.2 2.1 +/-0.3 2.2 +/-0.3 2.1 +/-0.3 2.1 +/- 0.3 2.3 +/- 0.3 1.9 +/- 0.3 2.2 +/- 0.3 2.2+/-0.3 2.3+/-0.3 1.8 +/-0.3 3.1 +/-0.3 3.1 +/-0.3 2.8 +/- 0.3 3.1 +/-0.3 4.3+/-0.3 1 Control Location 2 Sampler Malfunction; Loss of Data 57 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table B-6 -Continued Concentration of Beta Emitters in Air Particulates (Results in units of 10-2 pCi/m 3+/- 2cr)Start Date Stop Date SFA1 MET Station SFA2 1 Visitors Center SFA3 NNW of ISFSI SFA4 SSE of ISFSI 8/28/2006 9/4/2006 9/11/2006 9/18/2006 9/25/2006 10/2/2006 10/9/2006 10/16/2006 10/23/2006 10/30/2006 11/6/2006 11/13/2006 11/20/2006 11/27/2006 12/4/2006 12/12/2006 12/18/2006 12/25/2006 9/4/2006 9/11/2006 9/18/2006 9/25/2006 10/2/2006 10/9/2006 10/16/2006 10/23/2006 10/30/2006 11/6/2006 11/13/2006 11/20/2006 11/27/2006 12/4/2006 12/11/2006 12/18/2006 12/25/2006 1/1/2007 1.0 +/-0.2 2.2 +/- 0.2 0.9 +/- 0.2 1.5 +/- 0.2 1.4 +/- 0.2 1.7 +/-0.2 2.2 +/- 0.2 1.1 +/-0.2 1.3 +/- 0.2 2.6 +/- 0.2 1.2 +/- 0.2 1.7 +/- 0.2 1.5 +/- 0.2 2.0 +/- 0.2 2.4 +/- 0.2 3.4 +/- 0.2 1.6 +/- 0.2 2.0 +/- 0.2 0.7 +/-.0.2 2.3 +/- 0.2 1.0 +/- 0.2 1.6 +/- 0.2 1.5 +/- 0.2 1.3 +/- 0.2 2.4+/-0.2 1.3 +/- 0.2 1.2 +/- 0.2 2.8 +/- 0.2 1.1 +/-0.2 1.5 +/-0.2 1.6 +/- 0.2 2.1 +/-0.2 2.7+/-0.2 3.3 +/- 0.2 1.4 +/-0.2 2.1 +/-0.2 0.8 +/- 0.2 2.1 +/- 0.2 0.9 +/- 0.2 1.9 +/- 0.2 1.6 +/- 0.2 1.3 +/- 0.2 2.1 +/- 0.2 1.2 +/-0.2 1.6 +/-0.2 2.2 +/- 0.2 1.2 +/-0.1 1.4 +/- 0.2 1.4 +/- 0.2 1.8 +/- 0.2 2.4 +/- 0.2 3.1 +/-0.2 1.6 +/- 0.2 1.8 +/- 0.2 1.1 +/-0.2 3.6 +/- 0.4 1.7 +/- 0.3 2.4 +/- 0.3 2.3+/-0.3 2.5+/-0.3 3.9 +/- 0.4 2.3+/-0.3 1.5 +/-0.2 4.5+/-0.4 1.4 +/-0.2 1.7 +/- 0.2 1.9 +/- 0.2 2.2 +/- 0.2 3.1 +/-0.2 3.6 +/- 0.2 2.0 +/- 0.2 2.2 +/- 0.2 1 Control Location 58 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table B-7 Concentration of Gamma Emitters in Air Particulates (Results in units of 10-3 pCi/m 3+/- 2a)Sample Al Date Entrance to Camp, Conoy A2 Camp Conoy Siren A3 Bay Breeze Rd A4 Route 765 at Lusby A5 1 EOF 1/15/2006 2/15/2006 3/15/2006 4/15/2006 5/15/2006 6/15/2006 7/15/2006 8/15/2006 9/15/2006 10/15/2006 11/15/2006 12/15/2006
- k*t*k"************************"*Sample SFA1 SFA2 1 SFA3 SFA4 Date MET Station Visitors Center NNW of ISFSI SSE of ISFSI 1/15/2006
...2/15/2006
...3/15/2006
....4/15/2006
.....5/15/2006
.....6/15/2006
....7/15/2006
- * * *8/15/2006
...9/15/2006
....10/15/2006
.....11/15/2006
....12/15/2006
....1 Control Location All Non-Natural Gamma Emitters <MDA 59
.January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table B-8a Concentration of Gamma Emitters in Vegetation Samples (Results in units of pCi/kg (wet) +/- 2a)SAMPLE CODE Sample Date Sample Type Gamma Emitters Ibl" Bay Breeze Rd Ib2 Bay Breeze Rd Ib3 Bay Breeze Rd Ib4 Camp Conoy Entrance Ib5 Camp Conoy Entrance Ib6 Camp Conoy Entrance Ib7 1 EOF Ib8 1 EOF 6/26/2006 7/24/2006 10/2/2006 6/26/2006 7/24/2006 10/2/2006 6/26/2006 7/24/2006 10/2/2006 6/26/2006 7/24/2006 8/28/2006 10/2/2006 6/26/2006 7/24/2006 8/28/2006 10/2/2006 6/26/2006 7/24/2006 8/28/2006 10/2/2006 6/26/2006 7/24/2006 10/2/2006 6/26/2006 7/24/2006 10/2/2006 6/26/2006 7/24/2006 10/2/2006 Cabbage Collards Broccoli Collards Cauliflower Cabbage Broccoli Brussels sprouts Collards Cabbage Collards Collards Broccoli Collards Cauliflower Cabbage Cabbage Broccoli Brussels sprouts Broccoli Collards Cabbage Collards Broccoli Collards Cauliflower Cabbage Broccoli Brussels sproutsýCollards*k*t*k*t"**t*r*t"**k*r"*Ib9 'EOF 1 Control Location All Non-Natural Gamma Emitters <MDA 60 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table B-8b Concentration of Gamma Emitters in Vegetation From Locations Around the IFSFI (Results in units of pCi/kg (wet) +/- 2a)SAMPLE CODE Sample Date Gamma Emitters SFbl MET Station SFb2 1 Visitors Center SFb3 NNW of ISFSI SFb4 SSE of ISFSI SFb5 On Site before Entrance to Camp Conoy 3/6/2006 6/19/2006 10/6/2006 11/20/2006 3/6/2006 6/19/2006 10/6/2006 11/20/2006 3/6/2006 6/19/2006 10/6/2006 11/20/2006 3/6/2006 6/19/2006 10/6/2006 11/20/2006 3/6/2006 6/19/2006 10/6/2006 11/20/2006 1 Control Location All Non-Natural Gamma Emitters <MDA 61 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table B-9 Concentration of Gamma Emitters in Soil Samples From Locations Around the ISFSI (Results in units of pCi/kg (dry) +/- 2o SAMPLE CODE Sample Date Cs-1 37 Gamma Emitters SFS1 MET station SFS2 2 Visitors Center SFS3 NNW of ISFSI SFS4 SSE of ISFSI SFS5 Entrance to Camp Conoy 3/6/2006 6/19/2006 9/25/2006 11/20/2006 3/6/2006 6/19/2006 9/25/2006 11/20/2006 3/6/2006 6/19/2006 9/25/2006 11/20/2006 3/6/2006 6/19/2006 9/25/2006 11/20/2006 3/6/2006 6/19/2006 9/25/2006 11/20/2006 1 1 1 1 73 +/- 54 65 +/- 59 178 +/- 51-922 +/- 127 473 +/- 113 221 +/- 74 888 +/- 133 37 +/- 45 87 +/- 70 331 +/-63 198 +/- 55 142 +/-41 157 +/- 47*t*L*t*t*L*t 1This isotope <MDA 2 Control Location.All Non-Natural Gamma Emitters <MDA 62 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE B-10 Typical MDA Ranges for Gamma Spectrometry Selected Fish Shellfish Shoreline Vegetation Soil Particulates Selected Nuclides Na-22 Cr-51 Mn-54 Co-58 Fe-59 Co-60 Zn-65 Nb-95 Zr-95 Ru-1 06 Ag-11im Te-129m 1-131 Cs-1 34 Cs-1 37 Ba-1 40 La-140 Ce-144 Bay Water pCi/I 1.6-3.8 12-40 1.4-3.2 1.5 -4.0 3.5-11 1.5-3.7 3.3-7.9 1.7-5.8 2.8-6.9 12-26 1.2-2.9 18 -60 2.4-49 1.2 -2.6 1.2-3.0 7.3-66 3.2-29 7.1 -12 Fish pCi/kg 21-29 160- 166 16-20 20-23 53 -74 18-25 46 -62 25-31 35-44 131-149 15-18 247-280 99 -121 14-17 15-18 174-208 45-49 Shellfish pCi/kg 18 -30 118 -176 15-22 16-26 36 -65 18 -26 36 -57 20 -35 29-43 124- 185 15-18 192-284 30-89 13-19 15- 34 75-184 49 -74 42-49 Shoreline pCi/kg 28 -29 208-213 26 -30 28 -32 60 -77 27 -39 69- 97 34 -40 45 -62 224 -287 21-31 321 -367 50 -52 24-34.5 25-30 138 -150 75-75 101-111 Vegetation pCi/kg 16 -37 14- 164 13-28 13-26 28-69 15- 35 32 -73 13 -27 21 -48 108 -239 11 -25 135-281 11 -37 11 -24 1.5-26 41-109 17-51 49 -86 Soil pCi/kg 33 -95 203 -486 32-81 28 -79 65-174 23-97 67 -238 34 -93 53 -141 264 -643 29 -88 346 -855 32.7-179 27 -94 27 -72 112 -430 60-138 110 -245 Particulates 1 0-3 pCi/m 3 1.3-3.4 13 -39 1.2-6.2 1.4-3.4 3.7-8.2 1.3-3.3 3.0-6.9 2.1 -5.0 2.1 -6.4 10 -25 0.1 -2.6 19 -55 1 1.0-2.4 1.0-2.8 12 -84 8.7-19 2.8-8.2 1 The MDA range for 1-131 on a silver zeolite cartridge is typically 4.16 x 10-' to 3.40 x 10-2 63 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE B-11 Typical LLDs for Gamma Spectrometry Selected Bay Water Fish Shellfish Sediment Particulate Precipitation Vegetation Soil Well Water Nuclides pCi/I pCi/kg pCi/kg pCi/kg 10-3 pCi/m 3 pCi$I p-Ci/Kg pCi/Kg pCi/I Na-22 2.9 22 22 24 2.9 2.9 35 24 2.9 Cr-51 17 88 88 110 12 17 162 110 17 Mn-54 2.4 17 17 18 2.1 2.4 27 18 2.4 Co-58 .2.4 16 16 17 2.0 2.4 25 17 2.4 Fe-59 5.2 37 37 38 4.6 5.2 60 38 5.2 Co-60 2.8 22 22 21 2.7 2.8 33 21 2.8 Zn-65 5.6 23 23 54 2.8 5.6 66 54 5.6 Nb-95 2.2 15 15 18 1.9 2.2 25 18 2.2 Zr-95 3.8 27 27 29 3.3 3.8 44 29 3.8 Ru-106 20 135 135 146 17 20 223 146 20 Ag-110m 2.1 14 14 16 1.8 2.1 25 16 2.1 Te-129m 26 149 149 180 20 26 265 180 26 1-131 2.0 11 11 14 1.5" 2.0 20 14 2.0 Cs-134 2.2 15 15 20 1.9 2.2 24 20 2.2 Cs-137 2.3 15 15 17 1.8 2.3 27 17 2.3 Ba-140 7.3 48 48 54 6.1 7.3 80 54 7.3 La-140 .4.1 26 26 25 3.4 4.1 41 25 4.1 Ce-144 12 43 43 75 5.5 12 101 75 12 The LLD for 1-131 measured on a silver zeolite cartridge is 2.0 xl0 3 pCi/m3 64 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table B-12 Direct Radiation (Results in Units of mR/90 days +/- 2a)Site Code DR01 DR02 DR03 DR04 DR05 DR06 DR07 Location On Site, along Cliffs Route 765, Auto Dump Route 765, Giovanni's Tavern Route 765, across from White Sands Drive.Route 765, John's Creek Route 765 at Lusby Entrance to Camp Conoy Camp Conoy Rd at Emergency Siren Bay Breeze Rd Calvert Beach Rd and Decatur Street Dirt road off Mackall &Parren Rd Mackall & Bowen Rds First Quarter 12.51 +/- 1.12 10.39 +/- 0.86 10.26 +/- 0.44 12.44+/- 1.19 11.62 +/- 0.55 10.04 +/- 0.85 10.68 +/- 0.14 14.35 +/- 1.09 11.22 +/- 0.43 10.46 +/- 0.39 10.47 +/- 0.47 10.02 +/- 0.55 Second Quarter 13.51 +/- 2.89 9.77 +/- 0.37 10.27 +/- 0.92 11.35 +/- 0.96 10.78 +/- 0.67 9.67 +/- 0.68 9.53 +/- 0.86 13.83 +/- 1.72 10.62 +/- 0.86 10.15 +/- 0.84 10.51 +/- 0.85 10.20 +/- 0.27 Third Quarter 12.90 +/- 0.76 10.62 +/- 0.38 10.48 +/- 1.17 12.21 +/- 0.83 11.36 +/- 0.72 10.00+/- 1.12 10.14 +/- 0.52 14.86 +/- 1.54 11.35 +/- 1.66 10.51 +/- 1.56 10.65 +/- 0.70 10.41 +/- 1.03 Fourth Quarter 14.73 +/- 4.05 10.90 +1- 1.31 10.75 +/- 1.40 12.35 +/- 0.59 11.93 +/- 0.57 10.54 +/- 1.42 10.82 +/- 0.77 15.00 +/- 0.46 11.05 +/- 0.80 10.50 +/- 0.69 11.49 +/- 0.33 11.08+/- 1.12 DR08 DR09 DR10 DR1 1 DR12 65 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table B-12 Direct Radiation (Results in Units of mR/90 days +/- 2a)First Quarter Second Quarter 11.41+/- 1.01 11.43 +/- 1.09 Site Code DR1 3 DR14 DR15 DR16 DR17 DR1 8 DR1 9 DR20 DR21 1 DR22 1 DR23 1 Location Mackall Rd, near Wallville Rodney Point Mill Bridge & Turner Rds Across from Appeal School Cove Point & Little Cove Point Rds Cove Point Long Beach On site, near shore EOF Solomons Island 12.81 +/- 1.06 11.51 +/- 1.11 10.22 +/- 0.81 9.29 +/- 0.64 10.74 +/- 1.15 12.94 +/- 0.89 11.76 +/- 0.62 11.02 +1- 0.70 14.41 +/- 1.21 12.10 +/- 1.02 16.44 +/- 1.01.12.29+/-
1.65 11.51 +/- 0.90 10.29 +/- 0.49 12.30 +/- 1.97 9.58 +/- 0.97 10.59 +/- 1.33 12.79 +/- 0.89 11.59 +/- 1.38 11.00 +/- 0.50 15.21 +/- 0.54 13.02 +/- 0.85 17.23 +/- 1.20 Third Quarter 11.55 +/- 1.38 13.18 +/- 0.26 11.46 +/- 0.80 10.86 +/- 1.14 12.75 +/- 0.43 9.29 +/- 0.44 10.64 +/- 0.81 11.99 +/- 2.23 11.49 +/- 0.99 Fourth Quarter 11.94 +/- 1.15 13.62 +/- 1.28 12.27 +/- 1.16 10.78 +/- 1.14 12.33 +1- 0.95 9.56 +/- 0.98 11.19 +/- 0.45 12.74 +/- 0.74 11.78 +/- 0.71 10.17 +/- 0.34 14.93 +/- 2.79 13.19 +/- 1.57 16.22 +/- 2.32*Taylors Island MET Station SW of ISFSI 15.46 +/- 0.90 13.88 +/-0.99 15.84 +/- 1.16 DR30 SFDR01* Missing Data Control Location 66 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table B-12 Site Code SFDR02 SFDR03 SFDR04 SFDR05 SFDR06 SFDR07 1 SFDR08 SFDR09 SFDR10 SFDR11 SFDR12 SFDR13 SFDR14 SFDR15 SFDR16 SFDR17 SFDR18'Control Location Location-NNW of ISFSI North of ISFSI NE of ISFSI East of ISFSI ESE of ISFSI Visitor's Center NNW of ISFSI SSE of ISFSI NW of ISFSI WNW ISFSI WSW of ISFSI South of ISFSI SE of ISFSI ENE of ISFSI SSW of ISFSI NNE of ISFSI West of ISFSI Direct Radiation (Results in Units of mR/90 days +/- 2o')First Quarter Second Quarter 19.68 +1- 2.16 19.87 +/- 2.70 33.51 +/- 3.89 36.66 +1- 6.39 31.55 +1- 5.90 31.43 +/- 3.84.17.75+/-
1.33 21.56+/- 0.64 16.03 +/- 1.19 16.92 +/ 1.14 12.11 +/- 0.44 13.45+/- 1.74 29.45 +/- 3.36 29.68 +/- 3.41 16.97+/- 1.51 31.84 +Y- 1.71 35.74 +/- 4.16 38.50 +/- 12.67 30.39 +/- 4.52 27.81 +/- 2.06 29.12 +/- 2.22 31.00 +/- 10.41 21.88 +/- 4.16 32.59 +/- 7.53 19.62+/- 1.96 36.43 +/- 3.88 19.52 +/- 3.58 22.89 +/- 3.02 34.22 +/- 6.89 37.73 +/- 7.39 35.29 +/- 3.26 39.52 +/- 6.77 38.44 +/- 8.94 39.65 +/- 8.98 Third Quarter 21.72 +/- 2.52 34.78 +/- 7.47 26.37 +/- 3.98 21.37 +/- 1.40 17.79 +/- 1.26 12.72 +/- 1.07 32.58 +/- 1.16 29.95 +/- 3.42 32.65 +/- 7.74 30.78 +/- 7.27 31.32 +/- 6.86 32.25 +/- 3.52 32.69 +/- 1.13 24.37 +/- 3.19 37.23 +/- 4.32 37.24 +/- 4.27 37.46 +/- 6.26 Fourth Quarter 21.04 +/- 1.03 35.95 +/- 4.63 30.76 +/- 4.00 18.91 +/- 2.00 17.86 +/- 1.60 12.29 +/- 0.91 28.43 +/- 1.46 29.70 +/- 3.73 34.33 +/- 6.54 25.40 +/- 2.85 31.86 +/- 6.23 31.28 +/- 2.40 30.94 +/- 3.03-22.03 +/- 2.33 35.12 +/- 4.32 37.18+/- 6.40 42.06 +/- 6.04 67 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK)68 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 APPENDIX C Quality Assurance Program Appendix C is a summary of Constellation Energy laboratory's quality-assurance program. It consists of Table C-i which is a compilation of the results ofthe Constellation Energy Laboratory's participation in an intercomparison program with Environmental Resource Associates (ERA) located in Arvada, Colorado and Analytics, Inc. located in Atlanta, Georgia.It also includes Table C-2 which is a compilation of the results of the Constellation Energy Laboratory's participation in a split sample program with Teledyne Brown Engineering located in Knoxville, Tennessee and Table C-3 which is a list of typical MDAs achieved by Teledyne Brown for Gamma Spectroscopy.
All the Constellation Energy Laboratory's results contained in Table C-I generally agree with the intercomparison laboratorys' results within the range of +/-2 a of each other. In addition, all the sets of intercomparison results in the table are in full agreement when they were further evaluated using the NRC Resolution Test Criteria 1.The uncertainties for the Constellation Energy Laboratory's results and Analytics' results are +/-2a while the ERA laboratory's uncertainty is based on USEPA guidelines 2.All the results contained in Table C-2 agree within the range of +/-2 a of each other with their respective Constellation Energy Laboratory original, replicate and/or Teledyne Brown Engineering's split laboratory samples, except for the comparisons of two soil samples and a shoreline sample involving Cs-137 results. The original analysis of the soil sample from SFS2 collected on 3/06/2006, the split analysis of the soil sample from SFS4 collected on 6/19/2006, and the split analysis of the shoreline sample do not agree within the range of +/-2F of their respective QC comparison soil samples analyze&.
These minor discrepancies, which have been observed in previous reporting periods, are most probably due to counting statistics and/or the non-homogeneous nature of this type of sample.. Other samples whose nature generally precludes sample splitting are marked "**" in the SplitAnalysis column.NRC Inspection Manual, Inspection Procedure 84750, March 15, 1994 2 National Standards for Water Proficiency Testing Studies Criteria Document, December 1998 69 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK)70 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE OF CONTENTS -ANALYTICAL RESULTS Table Title Page C-1 Results of Participation in Cross Check Programs .............................................................
73 C-2 Results of Quality Assurance Program ................................................................................
76 C-3 Teledyne Brown Engineering's Typical MDAs for Gamma Spectrometry
...........................
85 71 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK)72 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE C-1 Results of Participation in Cross Check Programs Sample Sample Type Isotope Reported Cross Check Date and Units Observed Laboratory's Lab Results 1 Results 1 1/16/06 3/23/06 3/23/06 3/23/06 4/11/06 6/8/06 6/8/06 Water-pCi/L Milk-pCi/L Charcoal Cartridge-pCi Water-pCi/L Water-pCi/L Water-pCi Water-pCi/L Ba-1 33 Co-60 Cs-1 34 Cs-1 37 Zn-65 1-131 Cs-134 Cs-1 37 Ce-141 Cr-51 Mn-54 Co-58 Fe-59 Co-60 Zn-65 1-131 Gross 13 1-131 Gross 13 1-131 Cs-1 34 Cs-1 37 Ce-141 Co-58 Fe-59 Cr-51 Co-60 Mn-54 Zn-65 90+/-8 101+/-8 19+/-5 112+/-11 194+/-24 79+/-19 106+/-13 92+/-16 108+/-19 280+/-101 93+/-18 112+/-20 87+/-23 131+/-16 182+/-38 114+/-8 225+/-3 19+/-5 156+/-2 83+/-26 101+/-12 114+/-19 166+/-23 92+/-19 96+/-26 264+/-117 116+/-15 141+/-20 155+/-39 89+/-10 98+/-5 22+/-5 110+/-6 200+/-19 78+/-3 121+/-4 89+/-3 104+/-3 280+/-9 93+/-3 105+/-3 87+/-3 128+/-4 176+/-6-86+/-3 262+/-9 20+/-3 169+/-6 75+/-2 103+/-3 95+/-3 149+/-5 81+/-3.76+/-3-210+/-7 104+/-4 119+/-4 150+/-5' See discussion at the beginning of the Appendix.73 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE C-1 -Continued Results of Participation in Cross Check Programs Sample Date 6/8/06 7/10/06 7/10/06 9/14/06 9/14/06 Sample Type and Units Filter-pCi/filter Water-pCi/L Water-pCi/L Charcoal Cartridge-pCi Filter-pCi/filter Isotope Observed Ce-141 Cr-51 Cs-1 34 Cs-1 37 Mn-54 Fe-59 Zn-65 Co-60 Co-58 Ba-133 Cs-134 Cs-137 Zn-65 Co-60 Gross 13 1-131 Gross 13 Reported Laboratory's Results 1 134+/-7 200+/-35 71+/-5 82+/-7 105+/-8 70+/-8 143+/-16 90+/-6 71+/-7 80+/-14 46+/-9 243+/-23 113+/-32 101+/-13 7.46+/-3.00 111+/-8 80+/-2 Cross Check Lab Resultsl 129+/-4 182+/-6 89+/-3 82+/-3 130+/-3 66+/-2 130+/-4 90+/-3 70+/-2 85+/-9 52+/-5 239+/-12 128+/-12 103+/-5 8.95+/-5.00 92+/-3 85+/-3' See discussion at the beginning of the Appendix 74 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE C-I -Continued Results of Participation in Cross Check Programs Sample Sample Type Isotope Reported:
Cross Check Date and Units Observed Laboratory's Lab Results 1 Results!9/18/06 10/06/06 12/07/06 12/07/06 12/07/06 Filter-pCi/filter Water-pCi/L Milk-pCi/L Filter-pCi/filter Water-pCi/L Am-241 Cs-1 34 Cs-137 Co-60 1-131 1-131 Ce-141 Cr-51 Cs-1 34, Cs-1 37 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 Gross p 396+/-131 2789+/-42 251+/-18 1499+/-28 27+/-2, 86+/-56 369+/-39 607+/-200 150+/-15 264+/-29 96+/-18 140+/-23 80+/-29 184+/-39 331+/-26 216+/-9 323+/-50 81+/-5 163+/-10.54+/-8 81+/-9.60+/-12 112+/-18 191+/-10 255+/-3 297+/-116 2790+/-390, 208+/-66 1220+/-210 23+/-3 70+/-2 294+/-10 433+/-14 147+/-5 237+/-8 84+/-3 111+/-4 80+/-3 164+/-5 281+/-9 191+/-6 280+/-9 95+/-3 153+/-5 54+/-2 72+/-2 52+/-2 106+/-4 182+/-6:'225+/-7'See discussion at the beginning of the Appendix 75 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE C-2 Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split And Location Date Analysis Analysis Analysis Analysis 102 pCi/m 3 Air Iodine-A3 1/09/06 1-131 <MDA <MDA **Air Iodine-A4 1/09/06 1-131 <MDA <MDA **Air Filter -Al 1/09/06 Beta 1.7+/-0.2 1.9+/-0.2 **Air Filter -A2 1/09/06 Beta 1.5+/-0.1 1.6+/-0.2 **Air Filter -A3 1/09/06 Beta 1.1+/-0.2 1.4+/-0.2 **Air Filter -A4 1/09/06 Beta 1.7+/-0.2 1.9+/-0.2 **Air Filter -A5 1/09/06 Beta 1.5+/-0.2 1.6+/-0.2 **Air Filter -SFAI 1/09/06 Beta 1.6+/-0.3 1.7+/-0.2 **Air Filter -SFA2 1/09/06 Beta 1.4+/-0.2 1.6+/-0.2 **Air Filter -SFA3 1/09/06 Beta 1 1 **Air Filter -SFA4' 1/09/06 Beta 1.5+/-0.2 1.9+/-0.2 **10-2 pCi/m 3 Air Filter-Al 2/06/06 Beta 1.5+/-0.2 1.7+/-0.2 **Air Filter-A2 2/06/06 Beta 1.2+/-0.2 1.3+/-0.2 **Air Filter-A3 2/06/06 Beta 1.3+/-0.2 1.3+/-0.2 **Air Filter-A4 2/06/06 Beta 2.1+/-0.3 2.3+/-0.2 **Air Filter-A5 2/06/06 Beta 1.2+/-0.2 1.4+/-0.2 **Air Filter-SFAI 2/06/06 Beta 1.3+/-0.2 1.5+/-0.2 **Air Filter-SFA2 2/06/06 Beta 1.4+/-0.2 1.4+/-0.2 **Air Filter-SFA3 2/06/06 Beta 1.1+/-0.2 1.1+/-0.2 **Air Filter-SFA4 2/06/06 Beta 1.9+/-0.2 2.0+/-0.2 **Air Iodine-Al 2/06/06 1-131 <MDA <MDA **Air Iodine-A2 2/06/06 1-131 <MDA <MDA **pCi/L Bay Water-Wa2 2/28/06 Gamma <MDA <MDA <MDA" *The nature of these samples precluded splitting them with an independent laboratory.
1 Result is below laboratory's LLD for this analysis 76 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE C-2 -Continued Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split And Location Date Analysis Analysis Analysis Analysis 10-2 pCi/m 3 Air Filter-Al Air Filter-A2 Air Filter-A3 Air Filter-A4 Air Filter-A5 Air Filter-SFA1 Air Filter-SFA2 Air Filter-SFA3 Air Filter-SFA4 Air Iodine-A3 Air.lodine-A4 3/06/06 3/06/06 3/06/06 3/06/06 3/06/06 3/06/06 3/06/06 3/06/06 3/06/06 3/06/06 3/06/06 Beta Beta Beta Beta Beta Beta Beta Beta Beta 1-131 1-131 2.3+/-0.3 1.9+/-0.2 1.5+/-0.2 2.3+/-0.3 2.2+/-0.2 2.1+/-0.2 2.0+/-0.2 1.9+/-0.2 2.9+/-0.3 2.4+/-0.3 1.8+/-0.2 1.6+/-0.2 2.2+/-0.3 2.4+/-0.3 2.2+/-0.2 1.9+/-0.2 2.0+/-0.2 2.8+/-0.3**************<MDA < MDA< MDA < MDA Soil-SFS1 Soil-SFS2 Vegetation-SFbl Vegetation-SFb2 Oysters-la3 3/06/06 3/06/06 3/06/06 3/06/06 3/24/06 Gamma Cs-1 37 Gamma Gamma Gamma<MDA<MDA<MDA<MDA<MDA pCi/Kg<MDA 100+/-71.<MDA<MDA<MDA<MDA 142+/-92<MDA<MDA<MDA pCi/L<MDA Bay Water-Wa2 4/28/06 Gamma <MDA 10 Air Filter-Al 4/03/06 Beta 2.3+/-0.2 Air Filter-A2 4/03/06 Beta 2.1+/-0.2 Air Filter-A3 4/03/06 Beta 1.9+/-0.2 Air Filter-A4 4/03/06 Beta 2.3+/-0.2 Air Filter-A5 4/03/06 Beta 2.0+/-0.1 Air Filter-SFA1 4/03/06 Beta 2.6+/-0.2 Air Filter-SFA2 4/03/06 Beta 1.8+/-0.2 Air Filter-SFA3 4/03/06 Beta 2.0+/-0.2 Air Filter-SFA4 4/03/06 Beta 2.5+/-0.2**The nature of these samples precluded splitting them with an independent laboratory.
77<MDA ,)-2 pCi/m 3'2.4+/-0.2 1.8+/-0.2 1.7+/-0.2 2.1+/-0.2 2.1+/-0.1 2.4+/-0.2 1.9+/-0.2 1.9+/-0.2 2.2+/-0.2**************
January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE C-2 -Continued Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split And Location Date Analysis Analysis Analysis Analysis 10-2 pCi/m3 Air Iodine-Al 4/03/06 1-131 <MDA <MDA **Air Iodine-A2 4/03/06 1-131 <MDA <MDA **10-2 pCi/m 3 Air Filters-Al 4/15/06 Gamma <MDA <MDA <MDA Air Filters-A2 4/15/06 Gamma <MDA <MDA <MDA Air Filters-A3 4/15/06 Gamma <MDA <MDA <MDA Air Filters-A4 4/15/06 Gamma <MDA <MDA <MDA Air Filters-A5 4/15/06 Gamma <MDA <MDA <MDA Air Filters-SFA1 4/15/06 Gamma <MDA <MDA <MDA Air Filters-SFA2 4/15/06 Gamma <MDA <MDA <MDA Air Filters-SFA3 4/15/06 Gamma <MDA <MDA <MDA Air Filters-SFA4 4/15/06 Gamma <MDA <MDA <MDA 10-2 pCi/m 3 Air Iodine-A3 5/08/06 1-131 <MDA <MDA **Air Iodine-A4 5/08/06 1-131 <MDA <MDA **Air Filter-Al 5/08/06 Beta 1.4+/-0.2 1.3+/-0.2 Air Filter-A2 5/08/06 Beta 1.4+/-0.2 1.3+/-0.2 **Air Filter-A3 5/08/06 Beta 1 1 **Air Filter-A4 5/08/06 Beta 1.2+/-0.2 1.4+/-0.2 **Air Filter-A4 5/08/06 Beta 1.5+/-0.2 1.5+/-0.2 **Air Filter-SFA5 5/08/06 Beta 1.5+/-0.2 1.3+/-0.2 **Air Filter-SFA2 5/08/06 Beta 1.3+/-0.2 1.4+/-0.2 **Air Filter-SFA3 5/08/06 Beta 1.6+/-0.2 1.4+/-0.2 **Air Filter-SFA4 5/08/06 Beta 1.8+/-0.2 1.7+/-0.2 **pCi/L Bay Water-Wa2 5/31/06 Gamma <MDA <MDA <MDA**The nature of these samples precluded splitting them with an independent laboratory..
'Result is below laboratory's LLD for this analysis 78 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE C-2 -Continued Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split And Location Date Analysis Analysis Analysis Analysis 102 pCi/m 3 Air Iodine-Al Air Iodine-A2 6/05/06 6/05/06 1-131 1-131<MDA<MDA<MDA<MDA****10-2 pCi/m 3 Air Filter-Al Air Filter-A2 Air Filter-A3 Air Filter-A4 Air Filter-A5 Air Filter-SFA1 Air Filter-SFA2 Air Filter-SFA3 Air Filter-SFA4 Soil-SFS2 Soil-SFS4 Vegetation-SFb2 Vegetation-SFb4 Shoreline-Wbl 6/05/06 6/05/06 6/05/06 6/05/06 6/05/06 6/05/06 6/05/06 6/05/06 6105/06.Beta Beta Beta Beta Beta Beta Beta Beta Beta 1.5+/-0.2 1.8+/-0.2 1.9+/-0.3 1.4+/-0.2 2.0+/-0.2 1.8+/-0.2 1.7+/-0.2 1.2+/-0.2 2.1+/-0.3 1.3+/-0.2 1.5+/-0.2 1.7+/-0.2 1.3+/-0.2 1.7+/-0.2 1.6+/-0.2 1.7+/-0.2 1.4+/-0.2 2.0+/-0.3 pCi/Kg 101+/-77 88+/-67<MDA<MDA pCi/Kg<MDA********6/19/06 6/19/06 6/19/06 6/19/06 Cs-137 Cs-1 37 Gamma Gamma 73+/-54 86+/-70<MDA<MDA 176+/-86<MDA<MDA<MDA 6/26/06 Gamma<MDA 225+/-73 DR05 DR06 DR07 DR08 DR09 DR1 0 DR11 DR29 DR31 6/30/06 6/30/06 6/30/06 6/30/06 6/30/06 6/30/06 6/30/06 6/30/06 6/30/06 TLD TLD TLD TLD TLD TLD TLD TLD TLD 10.78+/-0.67 9.67+/-0.68 9.53+/-0.86 13.83+/-1.72 10.62+/-0.86 10.15+/-0.84 10.51+/-0.85 14.90+/-1.12 14.98+/-1.33 mR/90 Days 11.26+/-0.84 9.77+/-1.25 9.76+/-0.67 14.24+/-0.78 10.50+/-1.29 10.17+/-1.02 10.08+/-1.15 15.73+/-1.80 14.54+/-0.83
- The nature of these samples precluded splitting them with an independent laboratory.
79 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE C-2 -Continued Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split And Location Date Analysis Analysis Analysis Analysis mR/90 Days SFDR14 6/30/06 TLD 36.43+/-3.88 34.21+/-7.21
- SFDR15 6/30/06 TLD 22.89+/-3.02 23.66+/-6.11
- 10-2 pCi/m 3 Air Filter-Al 7/03/06 Beta 1.8+/-0.2 1.5+/-0.2 **Air Filter-A2 7/03/06 Beta 1.4+/-0.2 1.4+/-0.2 **Air Filter-A3 7/03/06 Beta 1.5+/-0.2 1.6+/-0.2 **Air Filter-A4 7/03/06 Beta 1.6+/-0.2 1.6+/-0.2 **Air Filter-A5 7/03/06 Beta 2.6+/-0.3 2.5+/-0.2 **Air Filter-SFA1 7/03/06 Beta 1.7+/-0.2 1.6+/-0.2 **Air Filter-SFA2 7/03/06 Beta 1.6+/-0.2 1.6+/-0.2 **Air Filter-SFA3 7/03/06 Beta 1.6+/-0.2 1.6+/-0.2 **Air Filter-SFA4 7/03/06 Beta 2.2+/-0.3 2.4+/-0.3 **Air Iodine-A3 7/03/06 1-131 <MDA <MDA **Air Iodine-A4 7/03/06 1-131 <MDA <MDA **pCi /kg Vegetation-lbl 7/24/06 Gamma <MDA <MDA <MDA Vegetation-lb2 7/24/06 Gamma <MDA <MDA <MDA Vegetation-1b4 7/24/06 Gamma <MDA <MDA <MDA Vegetation-lb5 7/24/06 Gamma <MDA <MDA <MDA Vegetation-lb7 7/24/06 Gamma <MDA <MDA <MDA Vegetation-lb8 7/24/06 Gamma <MDA <MDA <MDA 10-2 pCi/m 3 Air Filter-Al 8/07/06 Beta 1.8+/-0.2 1.8+/-0.2 **Air Filter-A2 8/07/06 Beta 2.4+/-0.3 2.5+/-0.3 **Air Filter-A3 8/07/06 Beta 2.6+/-0.3 2.3+/-0.3 **Air Filter-A4 8/07/06 Beta 2.1+/-0.2 1.8+/-0.2 **Air Filter-A5 8/07/06 Beta 2.7+/-0.3 3.0+/-0.3 **Air Filter-SFA1 8/07/06 Beta 1.6+/-0.2 1.8+/-0.2 **Air Filter-SFA2 8/07/06 Beta 2.4+/-0.2 2.4+/-0.2 **Air Filter-SFA3 8/07/06 Beta 2.3+/-0.2 2.1+/-0.2 **Air Filter-SFA4 8/07/06 Beta 3.1+/-0.3 3.3+/-0.4 ****The nature of these samples precluded splitting them with an independent laboratory.
80 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE C-2 -Continued Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split And Location Date Analysis Analysis Analysis Analysis 10.2 pCi/m 3.Air Iodine-Al 8/07/06 1-131 <MDA <MDA **Air Iodine-A2 8/07/06 1-131 <MDA <MDA *** pCi/kg, Fish-lal 8/22/06 Gamma <MDA <MDA <MDA Oysters-la3 8/22/06 Gamma <MDA <MDA <MDA pCi/L Bay Water-Wa2 8/31/06 Gamma <MDA <MDA <MDA 10-2 pCi/m3 Air Iodine-A3 9/04/06 1-131 <MDA <MDA **Air Iodine-A4 9/04/06 1-131 <MDA <MDA **Air Filter-Al 9/04/06 Beta 1.3+/-0.2 1.7+/-0.2 **Air Filter-A2 9/04/06 Beta 1.0+/-0.2 1.3+/-0.2 **Air Filter-A3, 9/04/06 Beta 1.0+/-0.2 1.3+/-0.2 **Air Filter-A4 9/04/06 Beta 0.9+/-0.2 1.2+/-0.2 **Air Filter-A5 9/04/06 Beta 1.1+/-0.2 1.3+/-0.3 **Air Filter-SFA1 9/04/06 Beta 1.0+/-0.2 1.1+/-0.2 **Air Filter-SFA2 9/04/06 Beta 0.7+/-0.2 0.9+/-0.2 **Air Filter-SFA3 9/04/06 Beta 0.8+/-0.2 1.2+/-0.2 **Air Filter-SFA4 9/04/06 Beta 1.1+/-0.2 1.6+/-0.3 **10-3 pCi/m 3 Air Filters-Al 9/15/06 Gamma <MDA <MDA <MDA.Air Filters-A2 9/15/06 Gamma <MDA <MDA <MDA Air Filters-A3 9/15/06 Gamma <MDA <MDA <MDA Air Filters-A4 9/15/06 Gamma <MDA <MDA <MDA Air Filters-A5 9/15/06 Gamma <MDA <MDA <MDA Air Filters-SFA1 9/15/06 Gamma <MDA <MDA <MDA Air Filters-SFA2 9/15/06 Gamma <MDA <MDA <MDA**The nature of these samples precluded splitting them with an independent laboratory.
81 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE C-2 -Continued Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split And Location Date Analysis Analysis Analysis Analysis 10-3 pCi/m 3 Air Filters-SFA3 Air Filters-SFA4 9/15/06 9/15/06 Gamma Gamma<MDA<MDA<MDA<MDA<MDA<MDA DR05 DR06 DR07 DR08 DR09 DR1 0 DR11 SFDR14 SFDR15 DR29 DR31 Vegetation-lbl Vegetation-lb2 Vegetation-lb4 Vegetation-lb5 Vegetation-lb7 Vegetation-lb8 Air Iodine-Al Air Iodine-A2 09/30/06 09/30/06 09/30/06 09/30/06 09/30/06 09/30/06 09/30/06 09/30/06 09/30/06 09/30/06 09/30/06 TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD 11.36+/-0.72 10.00+/-1.12 10.14+/-0.52 14.86+/-1.54 11.35+/-1.66 10.51+/-1.56 10.65+/-0.70 32.69+/-1.13 24.37+/-3.19 14.46+/-0.87 15.29+/-0.51 mR/90 Days 11.64+/-1.29 9.74+/-1.34 10.09+/-0.97 11.59+/-4.35 9.96+/-1.11 9.27+/-1.19 9.27+/-1.05 29.65+/-3.24 20.99+/-2.16 13.09+/-2.09 12.95+/-1.13
- 10/02/06 10/02/06 10/02/06 10/02/06 10/02/06 10/02/06 Gamma Gamma Gamma Gamma Gamma Gamma<MDA<MDA<MDA<MDA<MDA<MDA pCi/kg<MDA<MDA<MDA<MDA<MDA<MDA<MDA<MDA<MDA<MDA<MDA<MDA 10-2 pCi/m 3 10/09/06 10/09/06 1-131 1-131<MDA<MDA<MDA<MDA****The nature of these samples precluded splitting them with an independent laboratory.
82 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE C-2 -Continued Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split -And Location Date Analysis Analysis Analysis Analysis 10-2 pCi/m 3 Air Filter-Al 10/09/06 Beta 1.6+/-0.2 1.5+/-0.2 **Air Filter-A2 10/09/06 Beta 1.8+/-0.2 1.5+/-0.2 **Air Filter-A3 10/09/06 Beta 1.6+/-0.3 1.7+/-0.3 **Air Filter-A4 10/09/06 Beta 1.5+/-0.2 1.3+/-0.2 Air Filter-A5 10/09/06 Beta 2.1+/-0.3 2.0+/-0.3 **Air Filter-SFA1 10/09/06 Beta 1.7+/-0.2 1.4+/-0.2 **Air Filter-SFA2 10/09/06 Beta 1.3+/-0.2 1.4+/-0.2 **Air Filter-SFA3 10/09/06 Beta 1.3+/-0.2 1.2+/-0.2 **Air Filter-SFA4 10/09/06 Beta 2.5+/-0.3 2.2+/-0.3 **Air Filter-Al 11/05/06 Beta 1.9+/-0.2 2.2+/-0.2 **Air Filter-A2 11/05/06 Beta 2.3+/-0.3 2.3+/-0.2 **Air Filter-A3 11/05/06 Beta 2.3+/-0.4 2.2+/-0.2 **Air Filter-A4 11/05/06 Beta 2.1+/-0.2 2.5+/-0.2 **Air Filter-A5 11/05/06 Beta 2.0+/-0.2 2.0+/-0.2 **Air Filter-SFA1 11/05/06 Beta 2.3+/-0.2 2.2+/-0.3 **Air Filter-SFA2 11/05/06 Beta 2.2+/-0.2 2.2+/-0.2 **Air Filter-SFA3 11/05/06 Beta 1.9+/-0.2 2.1+/-0.2 **Air Filter-SFA4 11/05/06 Beta 2.3+/-0.2 2.3+/-0.2 **Air Iodine-A3 11/05/06 1-131 <MDA <MDA **Air Iodine-A5 11/05/06 1-131 <MDA <MDA **pCi/L Bay Water-Wa2 11/30/06 Gamma <MDA <MDA <MDA**The nature of these samples precluded splitting them with an independent laboratory-83 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE C-2 -Continued Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split And Location Date Analysis Analysis Analysis Analysis 10-2 pCi/m 3 Air Filter-Al Air Filter-A2 Air Filter-A3 Air Filter-A4 Air Filter-A5 Air Filter-SFA1 Air Filter-SFA2 Air Filter-SFA3 Air Filter-SFA4 12/04/06 12/04/06 12/04/06 12/04/06 12/04/06 12/04/06 12/04/06 12/04/06 12/04/06 Beta Beta Beta Beta Beta Beta Beta Beta Beta 1.4+/-0.2 1.9+/-0.2 1.8+/-0.2 1.9+/-0.2 2.0+/-0.2 2.0+/-0.2 2.1+/-0.2 1.8+/-0.2 2.2+/-0.2 1.6+/-0.2 1.9+/-0.2 1.7+/-0.2 2.3+/-0.2 2.0+/-0.2 1.9+/-0.2 1.9+/-0.2 2.0+/-0.2 1.8+/-0.2**************Air Iodine-Al 12/04/06 1-131 <MDA Air Iodine-A2 12/04/06 1-131 <MDA**The nature of these samples precluded splitting them with an independent laboratory
<MDA<MDA 84 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE C-3 Teledyne Brown Engineering's Typical MDAs for Gamma Spectrometry Selected Bay Water Fish Shellfish Sediment Vegetation Particulates Nuclides pCi/I pCi/kg pCi/kg pCi/kg pCi/kg 10-3 pCi/m 3 H-3 175 -- -- -- -- --Na-22 1 8 3 12 6 5 Cr-51 12 105 4 104 50 63 Mn-54 1 9 3 12 5 4 Co-58 1 9 4 9 4 5 Fe-59 3 28 9 24 10 12 Co-60 1 9 4 12 5 6 Zn-65 2 20 8 25 10 9 Nb-95 1 12 7 14 6 9 Zr-95 2 18 8 20 9 9 Ru-106 9 75 30 90 41 40 Ag-110m 1 10 10 10 5 4 Te-129m- 16 131 60 162 79 95 1-131 4 65 30 35 22 74 Cs-134 1. 8 4 10 5 4 Cs-137 1 9 4 10 5 4 BaLa-140 3 32 15 25 14 36 Ce-144 7 40 16 54 26 18 85 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK)86 January 1 -December 31, 2006'Docket Nos. 50-317/50-318/72-8 APPENDIX D Land Use Survey Appendix D contains the results of a Land Use Survey conducted around Calvert Cliffs Nuclear Power Plant during this operating period. A table listing the raw data of this survey and a discussion of the results are included in this appendix.Land Use Survey Discussion Di A Land Use Survey was conducted to identify, within a distance of 5 miles, the location of the Sector Resid nearest milk animal, the nearest residence, and SE-1 the nearest garden greater than 50 m 2 in each of SSE-the nine sectors over land. A detailed description.-
1.of the Land Use Survey is given in a separate SSW 1.document (Ref. 9). The position of the nearest SW 1 residence and garden in each sector out to 5 miles .is given in the adjacent table. There are no 1.animals producing milk for human consumption.
WNW 2.within the 5 mile radius. There was a new residence located within the 5-mile radius in the NW 2.SSW sector; however, its distance from the plant is the same as that-reported for the closest residence in that sector in 2005.istance From Plant (miles)ence' Garden 7 1.7 3- 1.3 8 1.8-5 1.7 1 11 2 1.4 3 1.5 5 2.5 1 2.1 The closest residence is situated in the SW sector and the nearest garden is also in the SW sector, which is one of the leastprevalent wind directions.
In the S, SSE, and SEsectors, there-is the highest probability of wind blowing from the direction of the plant. The two gardens used for vegetable samples by the REMP have been placed in the sectors with the highest X/Q. One sampling garden is located in the S sector at a distance of0.4 miles, and another is situated near the site boundary in the SSE sector. at a distance iof 1.6 miles from the plant. These two sampling sites are considered good indicator locations for radioactive depositions around the plant.The dose assessment using this operating period meteorological data was performed, and no significant impact from. the plant was found.87-January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK)88 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 APPENDIX E Additional Samples and Analysis Results Appendix E is a presentation of the analytical results for additional samples collected in the environs of CCNPP. These extra samples are not required by the ODCM (Ref. 6). Table E-1 lists the locations of all the additional samples and the remaining tables in this appendix provide the results. Some of these samples were collected and analyzed to maintain the historical continuity.
for samples and sampling pathways discontinued when the Environmental Technical Specifications were changed in March, 1985. Additionally, they include the PICs added for the ISFSI.Table E-4 through E- 10 contain analytical results for samples taken from the various radiological.
pathways (i.e., aquatic, atmospheric, terrestrial, and direct radiation) surrounding the plant. In..general these results continue the historical trends previously observed in the official sites of the CCNPP REMP and ISFSI.Table E-1 1 shows the direct radiation readings from TLDs placed at the perimeter of the Resin Storage Area which is a temporary waste resin storage and cask transfer area located to the west of the ISFSI facility.
The TLD values are somewhat higher than those in the REMP program due to their proximity to this source of the radiation.
However, when the direct radiation readings for the Resin Storage Area are compared with those from the ISFSI and Site Boundary TLDs, it is apparent that temporary storage of spent resin and cask transfers are having no significant, measurable effect on the environs surrounding CCNPP.89 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK)90 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE OF CONTENTS -ANALYTICAL RESULTS Table Title Page E-1 Locations of Non-Tech Spec Environmental Sampling Stations for Calvert Cliffs Nuclear P ow er P lant ..............................................................................................................................
92'E-2 Synopsis of 2006 Calvert Cliffs Nuclear Power Plant Non-Tech Spec Radiological Environmental M onitoring Program ..................................................................................
,93 E-3 Annual Summary for Calvert Cliffs Nuclear Power Plant Units 1 & 2 Non-Tech Spec Radiological Environmental Monitoring Program ...........................................................
94 E-4 Concentration of Gamma Emitters in Bottom Sediment ...................................................
95 E-5 Concentration of Iodine-131 in Filtered Air. .......................................................................
96 E-6 Concentration of Beta Emitters in Air Particulates
............................................................
98 E-7 Concentration of Gamma Emitters in Air Particulates
..........................................................
100 E-8 Concentration, of Tritium and Gamma Emitters in Taylors Island Well Water ...............
101 E-9 Direct Radiation as Measured in Pressurized Ion Chamber ..............................................
102 E -10 D irect R adiation ...... * .................
.............................................................................................
103 E- 11 Direct Radiation from Resin Storage Area ...........................................................................
104 91 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 TABLE E-1 Locations of Non-Tech Spec Environmental Sampling Stations for Calvert Cliffs Nuclear Power Plant Station Description Distance' Direction'(KM) (Miles) (Sector)A6 Long Beach 4.4 2.7 NW A7 Taylors Island, Carpenter's Property 12.6 7.8 ENE A8 Cambridge, U of MD Estuarine Center 32.0 19.9 NE DR24 Route 4 And Parran Road 3.0 1.9 SW DR25 Camp Conoy Guard House 1.0 0.6 S DR26 Route 235 & Clarks Landing Rd. 20.5 12.7 SW DR27 Route 231 & Route 4 23.0 14.3 NW DR28 Taylors Island Emergency Siren #35 12.3 7.6 ENE DR29 Taylors Island Emergency Siren #38 12.5 7.8 E DR31 Cambridge, U of MD Estuarine Center 32.0 19.9 NE DR32 Twining Property, Taylors Island 12.3 7.6 NE DR33 P.A. Ransome Property, Taylors Island 14.8 9.2 ESE DR34 Shoreline at Barge Road 0.2 0.1 NE OSGDR1 North of Old Steam Generator Storage Facility 0.3 0.2 SW OSGDR2 West of Old Steam Generator Storage Facility 0.3 0.2 SW PIC I Taylors Island, Carpenter's Property 12.6 7.8 ENE PIC2 On Site before Entrance to Camp Conoy 0.7 0.4 S PIC3 Meteorological Station 0.8 0.5 WSW PIC4 NNW of ISFSI 0.6 0.4 SW PIC5 SSE of ISFSI 0.6 0.4 SSW PIC8 CCNPP Visitor's Center 0.3 0.2 NW RPDR5 Resin Storage Area -North Fence Lower 0.7 0.4 SW RPDR6 Resin Storage Area -North Fence Upper 0.7 0.4 SW RPDR7 Resin Storage Area -West Fence Right 0.7 0.4 SW RPDR8 Resin Storage Area -West Fence Left 0.7 0.4 SW RPDR9 Resin Storage Area -South Fence Upper 0.7 0.4 SW RPDR1O Resin Storage Area- South Fence Lower 0.7 0.4 SW RPDR1 I Resin Storage Area -East Fence Left 0.7 0.4 SW RPDR12 Resin Storage Area -East Fence Right 0.7 0.4 SW Wbs2 Discharge Area 0.3 0.2 N Wbs4 Camp Conoy/Rocky Point 3.0 1.9 SE Wwl Taylors Island, Carpenter's Property 12.6 7.8 ENE Distance and direction from the central point between the two containment buildings.
92 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 I Table E-2 Synopsis of 2006 Calvert Cliffs Nuclear Power Plant Non-Tech Spec Radiological Environmental Monitoring Program Sample Type Sampling Frequency 1 Number of Locations Number Collected Analysis Analysis Frequency Number Analyzed Aquatic Environment Bottom Sediment Atmospheric Environment Air Iodine 2 Air Particulates 3 Direct Radiation Pressurized Ion Chamber Ambient Radiation Terrestrial Environment Ground water Q 2 4 Gamma Q 4 W W 7 3 360 154 1-131 Gross Beta Gamma W W MVC 360 154*36 72 480 M Q 6 72 480 Gamma TLD M Q 20 M 2 12 H-3 Gamma M M 12 12 1 W=weekly, M=monthly, Q=quarterly, SA=semiannual, A=annual, C=composite 2 The collection device, contains silver Zeolite 3 Beta counting is performed after >=72 hour decay. Gamma spectroscopy performed on monthly composites of weekly samples 93 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table E-3 Annual Summary for Calvert Cliffs Nuclear Power Plant Units 1 & 2 Non-Tech Spec Radiological Environmental Monitoring Program Medium or Pathway Sampled (Unit of Measurement)
Type and Total Number of Analyses Performed Lower Limit of Detection (LLD)Indicator Locations Mean (F)/Rangel Location with Highest Annual Mean Name/Distance
&Direction 2 Highest Annual Mean (F) / Range Control Locations Mean (F)/Range Aquatic Environment Bottom Sediment (pCi/kg)Gamma (4)Cs-1 37 17 232 (2/2)(186-278)Discharge Area Wbs2 0.3 km N 232 (2/2)(186-278)152 (2/2)(131-172.90)
Atmospheric Environment Air Particulates (10-2 pCi/m 3)Direct Radiation Ambient Radiation (mR/90 days)Pressurized Ion Chamber (mR/30 days)Gross Beta (154)0.5 1.7 (102/102)(0.7-3.9)21.27 (480/480)(7.53-64.06)
TLD (480)Long Beach A6 4.4 km NW East Fence Right RPDR12 km NNW of ISFSI PIC4 0.6 km SW 1.7 (52/52)(0.7-3.9)47.88 (24/24)(15.28-64.06) 11.32 (12/12)(10.99-11.72) 1.5 (52/52)(0.5-3.1)Ionization Chamber (72)7.40 (60/60)(4.26-13.04) 6.22 (12/12)(5.66-6.71)
Mean and range based upon detectable measurements only. Fraction (F) of detectable measurements at specified location is indicated in parentheses 2 From the centerpoint between the two containment buildings 94 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table E-4 Concentration of Gamma Emitters in Bottom Sediment (Results in units of pCi/kg (dry) +/- 2a)SAMPLE CODE Sample Date Cs-1 37 Gamma Emitters Wbs2 6/19/2006 186 +/-62 Discharge Area 10/26/2006 278 +/- 64 Wbs41 6/19/2006 173 +/- 62 Camp Conoy/ Rocky Point. 10/26/2006 131 +/-73 Control Location* All Non-Natural Gamma Emitters <MDA 95 P.January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table E-5 Concentration of Iodine-131 in Filtered Air (Results in units of 10-3 pCi/M 3+/- 2a)Start Date ' Stop Date A6 Long Beach A7 Taylors Island CAM SFA1 Cambridge MET Station SFA2 1 Visitors Center SFA3 NNW of ISFSI SFA4 SSE of ISFSI 1/2/2006 1/9/2006 1/16/2006 1/23/2006 1/30/2006 2/6/2006 2/13/2006 2/20/2006 2/27/2006 3/6/2006 3/13/2006 3/20/2006 3/27/2006 4/3/2006 4/10/2006 4/17/2006 4/24/2006 5/1/2006 5/8/2006 5/15/2006 5/22/2006 5/29/2006 6/5/2006 6/12/2006 6/19/2006 6/26/2006 7/3/2006 7/10/2006 7/17/2006 7/24/2006 8/1/2006 8/7/2006 8/14/2006 8/21/2006 1/9/2006 1/16/2006 1/23/2006 1/30/2006 2/6/2006 2/13/2006 2/20/2006 2/27/2006 3/6/2006 3/13/2006 3/20/2006 3/27/2006 4/3/2006 4/10/2006 4/17/2006 4/24/2006 5/1/2006 5/8/2006 5/15/2006 5/22/2006 5/29/2006 6/5/2006 6/12/2006 6/19/2006 6/26/2006 7/3/2006 7/10/2006 7/17/2006 7/24/2006 8/1/2006 8/7/2006 8/14/2006 8/21/2006 8/28/2006*************************t*t*t 2 2*t 2t 2 2*t*t*t*t*J**t*t*t"*"**t**'Control Location 2 Sampler malfunction; Loss of Data* <MDA 96 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table E-5 -Continued Concentration of Iodine-131 in Filtered Air (Results in units of 10-3 pCi/M 3+/- 2a)Start Date Stop Date A6 Long Beach A7 Taylors Island CAM SFA1 Cambridge MET.Station SFA2 1 Visitors Center SFA3 NNW of ISFSI SFA4 SSE of ISFSI 8/28/2006 9/4/2006 9/11/2006 9/18/2006 9/25/2006 10/2/2006' 10/9/2006 10/16/2006 10/23/2006 10/30/2006 11/6/2006 11/13/2006 11/20/2006 11/27/2006 12/5/2006 12/12/2006 12/18/2006 12/25/2006 9/4/2006 9/11/2006 9/18/2006 9/25/2006:
10/2/2006 10/9/2006 10/16/2006 10/23/2006 10/30/2006 11/6/2006 11/13/2006 11/20/2006 11/27/2006 12/4/2006 12/11/2006 12/18/2006 12/25/2006 1/1/2007*****"**t"**r"*"**k********************************1 Control Location*<MDA 97
'4 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table E-6 Concentration of Beta Emitters in Air Particulates (Results in units of 10-2 pCi/m 3+/- 2cr)Start Date Stop Date A6 Long Beach A7 1 Taylors Island CAM Cambridge 1/2/2006 1/9/2006 1/16/2006 1/23/2006 1/30/2006 2/6/2006 2/13/2006 2/20/2006 2/27/2006 3/6/2006 3/13/2006 3/20/2006 3/27/2006 4/3/2006 4/10/2006 4/17/2006 4/24/2006 5/1/2006 5/8/2006 5/15/2006 5/22/2006 5/29/2006 6/5/2006 6/12/2006 6/19/2006 6/26/2006 7/3/2006 7/10/2006 7/17/2006 7/24/2006 8/1/2006 8/7/2006 8/14/2006 8/21/2006 1/9/2006 1/16/2006 1/23/2006 1/30/2006 2/6/2006 2/13/2006 2/20/2006 2/27/2006 3/6/2006 3/13/2006 3/20/2006 3/27/2006 4/3/2006 4/10/2006 4/17/2006 4/24/2006 5/1/2006 5/8/2006 5/15/2006 5/22/2006 5/29/2006 6/5/2006 6/12/2006 6/19/2006 6/26/2006 7/3/2006 7/10/2006 7/17/2006 7/24/2006 7/31/2006 8/7/2006 8/14/2006 8/21/2006 8/28/2006 1.2 +/- 0.2 1.5 +/- 0.2 1.0 +/- 0.2 1.3 +/- 0.2 1.3 +/-0.2 1.7 +/- 0.2 2.2 +/- 0.2 2.0+/-0.2 1.9 +/-0.2 2.0 +/-0.2 2.3 +/- 0.2 1.8 +/- 0.3 1.9 +/-0.2 1.5 +/-0.2 1.8 +/- 0.2 1.2 +/- 0.2 2.7 +/- 0.3 2.8 +/- 0.4 1.0 +/- 0.2 1.1 +/-0.2 1.4 +/- 0.2 1.3 +/- 0.2 1.1 +/-0.2 1.3+/-0.2 0.7 +/- 0.1 1.3 +/- 0.2 1.3 +/- 0.2 1.9 +/- 0.2 1.0 +/- 0.2 1.9 +/- 0.2 1.8 +/- 0.2 2.1 +/-0.2 1.9 +/- 0.2 2.6+/-0.2 1.9 +/- 0.2 1.4 +/- 0.2 1.3 +/- 0.2 1.6 +/- 0.2 1.9 +/- 0.2 1.7 +/-0.2 2.9 +/- 0.3 2.5 +/- 0.3 2.4 +/- 0.3 2.2 +/- 0.3 2.8+/-0.3 1.4 +/- 0.2 1.6 +/- 0.2 1.4 +/- 0.2 1.3 +/- 0.2 0.9 +/- 0.2 1.6 +/- 0.2 1.6 +/- 0.2 1.1 +/-0.2 1.1 +/-0.2 1.9 +/- 0.2 1.1 +/-0.2 1.1 +/-0.2 1.1 +/-0.2 0.7 +/- 0.1 1.5 +/- 0.2 0.5+/-0.1 1.4 +/-0.2 1.5 +/-0.2 0.8 +/- 0.2 1.7 +/- 0.2 1.7 +/-0.2 1.6 +/-0.2 2.2+/-0.2 1.6 +/- 0.2 1.2 +/-0.2 1.0 +/-0.2 1.3 +/-0.2 -, 1.5 +/-0.2 1.5 +/-0.2 2.1 +/70.2 2.0 +/- 0.2 1.7 +/-0.2 2.0 +/-0.2 2.1 +/-0.2 1.0 +/-0.2 1.0 +/-0.2 1.3 +/- 0.2 1.6 +/- 0.2 1.4 +/- 0.3 2 1.3 "+1- 0.4 2 1.0 +/-0.2 1.5 +/-0.2 1.6 +/-0.2 0.9 +/-0.2 1.0 +/- 0.2 0.8 +/- 0.2 1.9 +/-0.3 1.5 +/-0.2 1.6 +/-0.2 1.8 +/- 0.2 1.7 +/- 0.4 1.3 +/-0.2 1.7 +/-0.2 1.6 +/-0.2 2.4 +/-0.2 1 Control Location 2 Sampler malfunction; Loss of Data 98 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table E-6 -Continued Concentration of Beta Emitters in Air Particulates (Results in units of 1072 pCi/m 3 +/- 2cr)Start Date Stop Date A6 A7 1 CAM Long Beach Taylors Island Cambridge 8/28/2006 9/4/2006 1.2 +/-0.2 0.5 +/-0.1 0.9 +/-0.2 9/4/2006 9/11/2006 2.0 +/-0.2 1.7 +/-0.2 1.8 +/-0.2 9/11/2006 9/18/2006 0.9 +/- 0.2 1.0 +/- 0.2 0.9 +/-0.2 9/18/2006 9/25/2006 1.7 +/-0.2 1.5 +/-0.2 1.9 +/-0.2 9/25/2006 10/2/2006 1.6 +/-0.2 1.5 +/-0.2 1.7 +/-0.2 10/2/2006 10/9/2006 1.4 +/-0.2 1.8 +/-0.2 2.4 +/-0.3 10/9/2006-10/16/2006 2.3 +/-0.2 1.7 +/-0.2 3.3 +/-0.3 10/16/2006
.10/23/2006 1.4 +/-.0.2 1.3 +/-0.2 1.8 +/-0.2 10/23/2006 10/30/2006 1.2 +/- 0.2- 1.1 +/- 0.2 1.8+/- 0.2 10/30/2006 11/6/2006 2.7+/-0.3 1.9+/-0.2 2.6+/-,0.2 11/6/2006 11/13/2006 1.4 +/- 0.2 0.9 +/- 0.2 1.2 +/- 0.2 11/13/2006 11/20/2006 1.7 +/- 0.2 1.3 +/- 0.2 1.8 +/-0.2 11/20/2006 11/27/2006 2.0+/-0.2 1.4+/-0.2 1.7+/-0.2 11/27/2006 12/4/2006 2.3+/-0.2 1.8+/-0.2 2.4+/-0.2 12/4/2006 12/11/2006 3.1 +/-0.3 2.1 +/-0.2 3.1 +/-0.2 12/12/2006 12/18/2006 3.9 +/- 0.2 3.1 +/- 0.2 3.4 +/- 0.2 12/18/2006 12/25/2006 2.0 +/-0.3 1.2 +/-0.2 1.4 +/-0.2 12/25/2006 1/1/2007 2.5 +/-0.2 1.5 +/-0.2 1.8 +/-0.2 99 C ,.January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table E-7 Concentration of Gamma Emitters in Air Particulates (Results in units of 10-3 pCi/m 3+/- 2a)Sample Date A6 Long Beach A7 1 Taylors Island CAM Cambridge 1/15/2006 2/15/2006 3/15/2006 4/15/2006 5/15/2006 6/15/2006 7/15/2006 8/15/2006 9/15/2006 10/15/2006 11/15/2006 12/15/2006
- 'Control Location* Non-Natural Gamma Emitters <MDA 100 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table E-8 Concentration of Tritium and Gamma Emitters in Taylors Island Well Water (Results in units of 10-3 pCi/m 3+/- 2ar)Sample Date H-3 Gamma Emitters 1/31/2006 2/28/2006 3/29/2006 05/02/2006 5/31/2006 7/03/2006 8/1/2006 8/29/2006 9/26/2006 10/31/2006 11/28/2006 12/27/2006
<460<461<456<460<460<457<340<344<340<340<340<340"**t*k*t*** Non-Natural Gamma Emitters <MDA 101
- 1 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table E-9 Direct Radiation as Measured in Pressurized Ion Chamber (Results in units of mR/30 days +/- 10%)Sample Code Month Month PIC1 1 Taylor's Island PIC2 Entrance to Camp Conoy PIC3 MET Station PIC4 NNW of ISFSI PIC5 SSE of ISFSI PIC8 Visitor's Center JAN MAR MAY JUL SEP NOV JAN MAR MAY JUL SEP NOV JAN MAR MAY JUL SEP NOV JAN MAR MAY JUL SEP NOV JAN MAR MAY JUL SEP NOV JAN MAR MAY JUL SEP NOV 6.03 +/- 0.60 6.71 +/- 0.67 6.51 +/- 0.60 5.83 +/- 0.60 6.33 +/- 0.63 5.66 +/- 0.57 4.30 +/- 0.43 4.93 +/- 0.49 4.38 +/- 0.44 4.33 +/- 0.40 4.30 +/- 0.43 4.26 +/- 0.43 5.07 +/- 0.51 5.24 +/- 0.52 5.51 +/- 0.55 5.72 +/- 0.60 5.58 +/- 0.56 5.94 +/-0.59 11.14 +/- 1.11 11.55 +/- 1.16 11.60 +/- 1.16 11.03 +/- 1.10 11.00 +/- 1.10 11.39 +/- 1.14 6.62 +/- 0.66 9.19 +/- 0.92 12.53 +/- 1.25 11.61 +/- 1.16 11.24 +/-1.12 10.89 +/- 1.09 4.88 +/- 0.49 5.22 +/- 0.52 5.58 +/- 0.56 4.97 +/- 0.50 4.91 +/- 0.49 4.87 +/- 0.49 FEB APR JUN AUG OCT DEC FEB APR JUN AUG OCT DEC FEB APR JUN AUG OCT DEC FEB APR JUN, AUG OCT DEC FEB APR JUN AUG OCT DEC FEB APR JUN AUG OCT DEC 6.40 +/- 0.64 6.68 +/- 0.67 6.64 +/- 0.66 6.32 +/- 0.63 5.84 +/- 0.58 5.70 +/- 0.57 4.30 +/- 0.43 4.37 +/- 0.44 4.38 +/- 0.44 4.37 +/- 0.44 4.33 +/- 0.43 4.27 +/- 0.43 5.06 +/- 0.51 5.36 +/- 0.54 5.89 +/- 0.59 5.67 +/- 0.57 5.60 +/- 0.56 5.96 +/- 0.60 11.20 +/- 1.12 11.72 +/- 1.17 11.51 +/-1.15 11.13 +/- 1.13 10.99 +/- 1.10 11.55 +/-1.16 6.61 +/- 0.66 13.04 +/- 1.30 12.11 +/- 1.21 11.78 +/- 1.18 11.22 +/- 1.12 10.82 +/- 1.08 4.93 +/- 0.49 5.63 +/- 0.56 5.34 +/- 0.53 5.06 +/- 0.51 4.95 +/- 0.50 4.89 +/- 0.49 1 Control Location 102
--January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table E-10 Direct Radiation (Results in units of mR/90 days +/- 2cT)Site Code Location First Quarter Second Quarter Third Quarter Fourth Quarter DR24 DR25 DR26 DR27 DR28 DR29 DR31 DR32 DR33 DR34 OSG1 OSG2 Rt. 4 and Parran Rd.Camp Conoy Guard House Rt. 235 and Clark's Landing Road Rt. 231 and Rt. 4 Taylors Is. Siren #35 Taylors Is. Siren #38 Cambridge Twining Property, Taylors Island P. A. Ransome Property Shoreline at Barge Rd.North of Old Steam Generator Storage Facility West of Old Steam Generator Storage Facility 11.84 +/- 0.66 12.30 +/- 1.16 10.43 +/- 0.66 10.96 +/- 0.56 12.99 +1-.11 14.65 +/- 2.26 14.60 +1- 1.27 13.24 +/- 1.04 14.57 +/- 2.18 9.48 +/- 0.38 17.83 +/- 1.46 15.35 +/- 1.97 10.96 +1- 1.08 11.75 +/- 0.99 10.64 +/- 1.14 10.36 +/- 1.16 13.29 +/- 1.63 14.90 +/- 1.12 14.98 +/- 1.33 13.83 +/- 2.23 15.34 +/- 0.76 9.42 +/- 0.73 18.98 +/- 1.25 16.71 +/- 2.15 10.97 +/- 0.35 11.93 +/-1.11 10.43 +/- 0.84 10.77 +/- 0.99 13.91 +/- 1.59 14.46 +/- 0.87 15.29 +/- 0.51 14.28 +/- 0.78 15.22 +/- 1.62 9.53 +/- 0.83 18.97 +/- 1.80 16.65 +/- 2.00 11.68 +/- 1.09 12.72 +/- 1.30 10.70 +/- 0.81 11.25 +/- 1.01 13.36 +/- 1.76 13.37 +/- 1.61 15.90 */'2.56 13.32 +/- 1.61 15.16 +/- 2.18 9.55 +/- 0.88 19.51 +/-1.61 17.18 +/- 2.21 103 January 1 -December 31, 2006 Docket Nos. 50-317/50-318/72-8 Table E-11 Direct Radiation from Resin Storage Area (Results in units of mR/90 days +/- 2a)Site Code Location First Quarter Second Quarter Third Quarter Fourth Quarter RPDR05 RPDR06 RPDR07 RPDR08 RPDR09 RPDR10 RPDR11 RPDR12 North Fence Lower North Fence Upper West Fence Right West Fence Left South Fence Upper South Fence Lower East Fence Left East Fence Right 18.88 +/- 2.01 19.86 +/- 1.10 30.46 +/- 2.75 57.86 +/- 5.90 35.99 +/- 2.82 26.36 +/- 2.37 22.10 +/- 2.18 52.61 ÷/- 3.24 47.30 +/- 3.01 33.37 +/- 4.48 51.29 +1- 3.73 55.47 +/- 2.06 46.58 +/- 3.48 37.41 +/- 3.86 24.54 +1- 3.35 64.06 +/- 1.71 28.68 +/- 1.21 28.57 +/- 2.05 16.17 +/- 2.08 7.53 +/- 0.65 54.42 +/- 2.27 42.34 +/- 4.00 46.06 +/- 5.78 59.57 +/- 2.16 36.75 +/- 3.57 40.82 +1- 4.65 8.05 +/- 0.63 10.35 +/- 0.35 12.63 +/- 1.38 10.82 +/- 0.78 14.08 +/- 1.26 15.28 +/- 1.13 104