Text

Independent Spent Fuel Storage Installation - Radiological Environmental Monitoring Program Annual Report
	ML041380033
Person / Time
Site:	Calvert Cliffs
Issue date:	05/12/2004
From:	Tonacci M; Constellation Energy Group, Constellation Generation Group
To:	; Document Control Desk, Office of Nuclear Reactor Regulation
References
	+KBR1SISP20050504, -RFPFR
	Download: ML041380033 (111)
	v • d • e

Calvert Cliffs Nuclear Power Plant 1650 Calvert Cliffs Parkway Constellation Generation Group, LLC Lusby, Maryland 20657 Constellation I Energy Group May 12, 2004 U. S. Nuclear Regulatory Commission Washington, DC 20555 ATTENTION: Document Control Desk

SUBJECT:

Calvert Cliffs Nuclear Power Plant; Unit Nos. 1 & 2; Docket Nos. 50-317 & 50-318 Independent Spent Fuel Storage Installation; Docket No. 72-8 Radiological Environmental Monitoring Program Annual 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 Monitoring Report, dated April 2004.

Should you have questions regarding this matter, we will be pleased to discuss them with you.

Very truly yours, Mark E. Tonacci General Supervisor-Chemistry MET/CAN/bjd

Attachment:

As stated cc: J. Petro, Esquire H. J. Miller, NRC J. E. Silberg, Esquire Resident Inspector, NRC Director, Project Directorate I-l, NRC R. I. McLean, DNR G. S. Vissing, NRC P. Perzynski, MDE I*6~~

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, 2003 A. M Barnett L. J. Bartal, Ph.D.

R. L. Conatser A. J. Kaupa CONSTELLATION ENERGY CONSTELLATION GENERATION GROUP, LLC APRIL 2004

(LEFT BLANK)

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 TABLE OF CONTENTS LIST OF FIGURES .................................................................... iii LIST OF TABLES ...................................................................... v I.

SUMMARY

...................................................................... I II. CALVERT CLIFFS NUCLEAR POWER PLANT RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ............................................................. 3 II.A. INTRODUCTION ................................................................................... 3 II.B. PROGRAM ......... .......................................................................... 3 II.B.I Obiectives .......... .......................................................................... 3 1I.B.2 Sample Collection .................................................................................... 4 II.B.3 Data Interpretation ................................................................................... 4 II.B.4 Pro eram Exceptions .................................................................................... 4 II.C. RESULTS AND DISCUSSIONS ................. 4.......................

II.C.1 Aquatic Environment .................................................................................... 5 IIC.I.a Bay Water ..................................................................................... 5 II.C.1.b A uatic Organisms .................................................................................... 5 II.C. I.c Shoreline Sediment ............. 6..........................

I.C.2 Atmospheric Environment .................................................................................... 9 II.C.2.a Air Particulate Filters .................................................................................... 9 II.C.2.b Air Iodine .................................................................................... 9 II.C.3 Terrestrial Environment .................................................................................... 9 II.C.3.a Vegetation ................................................................................... 11 II.C.4 Direct Radiation ................................................................................... I I II.D. CONCLUSION ................................................................................... 13 III. INDEPENDENT SPENT FUEL STORAGE INSTALLATION RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ........................................................... 21 III.A. INTRODUCTION ................................................................................... 21 M .B PROGRAM . ................................................................................... 22 III.B.1 Obiectives ................................................................................... 22 III.B.2 Sample Collection ................................................................................... 22 III.B.3 Data Interpretation ................................................................................... 22 III.B.4 Proram Exceptions .................................................................................... 22 HII.C. RESULTS AND DISCUSSIONS ................................................................................... 22 III.C. I Atmospheric Environment ................................................................................... 23 III.C. I.a Air Particulate Filters ................................................................................... 23 III.C.2 Terrestrial Environment ................................................................................... 23 III.C.2.a Vegetation ................................................................................... 23 III.C.2.b Soils ......... .......................................................................... 24 III.C.3 Direct Radiation ................................................................................... 24 III.D. CONCLUSION ................................................................................... 25 IV. REFERENCES .................................................................... 29 APPENDIX A Sample Locations for the REMP and the ISFSI ................................................... 31 APPENDIX B Analysis Results for the REMP and the ISFSI ..................................................... 45 APPENDIX C Oualitv Assurance Program ..................................................................... 69 APPENDIX D Land Use Survey ..................................................................... 85 APPENDIX E Additional Samples and Analysis Results ............................................................. 87 i

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK) ii

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 LIST OF FIGURES Figure Title Page I Tritium in Plant Effluents and Chesapeake Bay Water ............................................................. 7 2 Silver-il10m and Potassium-40 in Chesapeake Bay Oysters .................................................... 8 3 Background Activity in the Calvert Cliffs Area ................................................................ 10 4 Mean TLD Gamma Dose, Calvert Cliffs Nuclear Power Plant ............................................... 12 5 Atmospheric Dispersion Around CCNPP Average Relative Air Concentrations .......... ......... l 5 6 Atmospheric Dispersion Around CCNPP Average Relative Ground Deposition ................... 17 7 Mean TLD Gamma Dose, ISFSI ............................................................... 26 A-1 Map of Southern Maryland and Chesapeake Bay Showing Location of Calvert Cliffs Nuclear Power Plant ................................................................ 38 A-2 Calvert Cliffs Nuclear Power Plant Sampling Locations, 0-2 Miles ....................................... 39 A-3 Calvert Cliffs Nuclear Power Plant Sampling Locations, 0-10 Miles ..................................... 41 A-4 Independent Spent Fuel Storage Installation Sampling Locations ........................................... 44 A-5 Enlarged Map of the Independent Spent Fuel Storage Installation Sampling Locations ......... 45 iii

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK) iv

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 LIST OF TABLES Table Title Page I Synopsis of 2003 Calvert Cliffs Nuclear Power Plant Radiological Environmental Monitoring Program................................................................................................................................................

.19 2 Annual Summary of Radioactivity in the Environs of the Calvert Cliffs Nuclear Power Plant Units I and 2....... 20 3 Synopsis of 2003 Calvert Cliffs Nuclear Power Plant Independent Spent Fuel Storage Installation Radiological Environmental Monitoring Program .27 A-1 Locations of Environmental Sampling Stations for the Calvert Cliffs Nuclear Power Plant .35 A-2 Locations of Environmental Sampling Stations for the Independent Spent Fuel Storage Installation at Calvert Cliffs .41 B-i Concentration of Tritium and Gamma Emitters in Bay Water .48 B-2 Concentration of Gamma Emitters in the Flesh of Edible Fish .49 B-3 Concentration of Gamma Emitters in Oyster Samples .50 B-4 Concentration of Gamma Emitters in Shoreline Sediment .51 B-5 Concentration of Iodine-131 in Filtered Air .52 B-6 Concentration of Beta Emitters in Air Particulates .54 B-7 Concentration of Gamma Emitters in Air Particulates .58 B-8a Concentration of Gamma Emitters in Vegetation Samples .59 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 .63 B-1i Typical LLDs for Gamma Spectrometry .64 B-12 Direct Radiation .65 C-1 Results of Participation in Cross Check Programs .73 C-2 Results of Quality Assurance Program .74 C-3 Teledyne Brown Engineering's Typical MDAs for Gamma Spectrometry .83 D-l Land Use Survey .85 E- 1 Locations of Non-ODCM Environmental Sampling Stations for Calvert Cliffs Nuclear Power Plant .. 90 E-2 Synopsis of 2003 Calvert Cliffs Nuclear Power Plant Non-ODCM Radiological Environmental Monitoring Program ............. 91 E-3 Annual Summary for Calvert Cliffs Nuclear Power Plant Units 1 & 2 Non-ODCM Radiological Environmental Monitoring Program .92 E-4 Concentration of Gamma Emitters in Bottom Sediment .93 E-5 Concentration of Iodine-1 31 in Filtered Air .94 E-6 Concentration of Beta Emitters in Air Particulates .96 E-7 Concentration of Gamma Emitters in Air Particulates .98 E-8 Concentration of Tritium and Gamma Emitters in Taylors Island Well Water .99 E-9 Direct Radiation as Measured in Pressurized Ion Chamber .100 E-10 Direct Radiation .101 E-l I Direct Radiation from Resin Storage Area .102 V

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK) vi

January 1 - December 31, 2003 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 3391 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. 2) and the Environmental and Independent Spent Fuel Storage Installation (ISFSI) Technical Specifications (Ref. 1, 6). 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 652 radiochemical analyses were performed on 584 environmental samples, and 546 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. 2) and the Environmental Technical Specifications (Ref. 1).

For the ISFSI monitoring program, 355 radiochemical analyses were performed on 295 environmental samples, 49 of which were in common with the original REMP. In addition, 438 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. 2) and the ISFSI Technical Specifications (Ref. 6).

In addition, 584 analyses were performed on 536 additional environmental samples, and 474 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, 204 radiochemical analyses were performed on 188 quality assurance samples and 66 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 samples. Bay water was analyzed for tritium and gamma emitters. Fish, oysters, and shoreline sediments were analyzed for gamma emitting radionuclides.

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 I

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 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 I-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 3391 radiological analyses performed. Low levels of various man-made fission and activation products were also observed in 34 of these analyses. Twenty-nine of these observations were attributed to fallout from past atmospheric weapons testing, while five analyses yielded low level positive results for the presence of H-3, which were attributable to plant operation. 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 5.84 x 10-3 mrem via liquid and gaseous pathways, which is less than 0.01% of the acceptable limit of 75 mrem/yr as specified in 40 CFR Part 190;

b. a maximum whole body dose of 4.19 x 10-3 mrem via liquid and gaseous pathways, which is less than 0.02% of the acceptable limit of 25 mremlyr as specified in 40 CFR Part 190;

c. a maximum calculated dose to all other organs via liquid and gaseous pathways was equal to 2.26 x 10-2 mrem to the GI-Tract. This dose is less than 0.1 % of the allowable limit of 25 mrem/yr as specified in 40 CFR Part 190.

Thus, it is concluded based upon the levels of radioactivity observed and the various dose calculations performed, that CCNPP Units 1 and 2 and the ISFSI did not cause any significant radiological impact on the surrounding environment.

2

January 1 - December 31, 2003 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-1, page 38.

Results of the monitoring program for the pre-operational and previous operational periods through December 31, 2002 have been reported 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 the body 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.

II.B. PROGRAM ll.B.1 Objectives 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. 2) 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 I - December 31, 2003 Docket Nos. 50-317/50-318/72-8 ll.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. 3).

ll.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.

ll.B.4 Pro2ram Exceptions There were no program exceptions for this operating period.

II.C. RESULTS AND DISCUSSIONS All the environmental samples collected during the year were analyzed using Constellation Energy laboratory procedures (Ref. 4). 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, 2003 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.

IIC. .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). The samples were obtained from a composite sampling system operating at 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, showed the presence of tritium in the Discharge (Wa2) samples in all four quarters and in the Intake (Wal) in only one of the four quarters. It is not unusual to observe concentrations of tritium occasionally in the Intake as a result of bay water recirculation. The detectable concentrations observed in the Discharge ranged from 207 +/-41 to 767 +/-44 pCi/L, and in the Intake ranged from less then detectable to 53 +39 pCi/L which are similar to those ranges observed in previous years.

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.

ll.C.L.b Aquatic Organisms Six 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 Ial and Ia2) and from the Patuxent River (sample codes Ia4 and LaS). 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 1a3) and Kenwood Beach (la6).

Edible portion of the fish and oyster samples were analyzed for gamma emitters.

5

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 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.

ll.C. 1 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.

6

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 FIGURE 1 Tritium in Plant Effluents and Chesapeake Bay Water 1200-1000-011 800 -

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January I - December 31, 2003 Docket Nos. 50-317/50-318/72-8 FIGURE 2 Silver-1IOm and Potassium-40 in Chesapeake Bay Oysters 0.2 1 I 0.18 -

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8

January 1 - December 31, 2003 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 AS).

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 0.2 x 10-2 to 3.0 x 10-2 pCi/m 3 for the indicator locations and 0.5 x 10-2 to 2.2 x 10-2 pCi/m 3 at the control lo-cation. The location with the highest overall mean of 1.7x10-2 pCi/m 3 was A4, Route 765 at Lusby.

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 I- 13 1.

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.

9

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 FIGURE 3 Background Activity in the Calvert Cliffs Area SURFACE AIR VAPORS, LUSBY, MD (A4) 250 l 200 E

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January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 II.C.3.a Vegetation Nine vegetation samples were collected from three locations during the year. These locations are Garden Plot off Bay Breeze Road (sample codes Ibl, 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 1b9). These samples were analyzed for gamma emitters, including analyses for I-131.

All samples showed detectable amounts of naturally occurring K-40 and Be-7. No plant related radionuclides were found in any of these samples.

11.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 DRI 3), 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 DRI 7), Cove Point (sample code DRI 8), Long Beach (sample code DRI9), and On Site Near Shore (sample code DR20). The three control locations are the Emergency Operations Facility (sample code DR2 1), 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 12.02 mR and ranged from 9.38 to 16.01 mR as reported in Table 2. The control locations showed a 90 day mean of 13.39 mR with ranges from 9.95 to 17.15 mR. The location with the highest overall mean of 15.96 was DR23, Taylors Island, Carpenters Property, which ranged from 14.49 to 17.15 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.

11

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 FIGURE 4 Mean TLD Gamma Dose, Calvert Cliffs Nuclear Power Plant 6 -

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January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 ILD. CONCLUSION Low levels of two man-made fission products were observed in the environment surrounding the plant, i.e. Cs-137 and tritium. The Cs-137 observations were attributed to fallout from past atmospheric weapons testing. Tritium was related to the operation of the plant (e.g., tritium in quarterly composited bay water samples).

Historical trends for tritium in bay water, Ag-I 10m and K-40 in oyster samples, background activity 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 4.84 x 10-3 mrem to a child via the plume, ground, vegetable, meat, and inhalation pathways at 1.7 km SW of Calvert Cliffs. This is less than 0.01% of the acceptable limit of 75 mrem/yr as specified in 40 CFR Part 190, "Environmental Radiation Protection Standards for Nuclear Power Operations."

A maximum whole body gamma dose of 2.35 x 10-3 mrem to a child at 1.7 km SW of Calvert Cliffs, which is less than 0.01% of the acceptable dose limit of 25 mrem/yr as specified in 40 CFR Part 190.

A maximum dose to any other organ, in this case the skin, of 2.84 x 10-3 mrem to all age groups at 1.7 km SW of Calvert Cliffs. This is about 0.01% of the acceptable dose limit of 25 mrem/yr as specified in 40 CFR Part 190.

Liquid Pathways A maximum thyroid dose of 1.00 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 40 CFR Part 190.

A maximum whole body dose of 1.84 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 40 CFR Part 190.

13

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 A maximum dose to any organ, in this case the GI-Tract, of 2.26 x 10-2 mR to an adult for all pathways, which is less than 0.1% of the acceptable dose limit of 25 mrem/yr specified in 40 CFR Part 190.

Gaseous and Liquid Pathways Combined A maximum thyroid dose of 5.84 x 10-3 mrem via liquid and gaseous pathways, which is less than 0.01% of the acceptable limit of 75 mrem/yr as specified in 40 CFR Part 190; A maximum whole body dose of 4.19 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 40 CFR Part 190; A maximum calculated dose to all other organs via liquid and gaseous pathways was equal to 2.26 x 10-2 mrem to the GI-Tract. This dose is less than 0.1% of the allowable limit of 25 mrem/yr as specified in 40 CFR Part 190.

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 & 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.

14

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 FIGURE 5 Atmospheric Dispersion Around CCNPP Average Relative Air Concentrations

ECFLUERT CLIFFS E:TIME INTEGRATED ELEUATED RUERAGE 03/06/04 15;28 X/O 1:84g7.00 HOUR INTEGRATION;RELEASE P V1 SCALE;m Ph4 -

2.00 lILES MODEL: TIME INTEGRATED STRAIGHT LINE START DOSE INTEGRATION; 01/01/03 01;00 END DOSE INTEGRATION: 12/31/03 24:00 CONTOUR Yin LEGEND (SEC/MB) p E.0E-07t 1 .0E-07-22.0E-07 7.8E-08-1 .0E-07

4. 0E-02-7.0E-02

2. E-82-4.OE-B9 1 .8E-08-2.8E-08 7.0E-W9-1 .E-08 15 0-01,

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK) 16

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 FIGURE 6 Atmospheric Dispersion Around CCNPP Average Relative Ground Deposition SITE;:CALUERT CLIFFS 03/06/04 15;23 TITLE: TIME INTEGRATED DEPOSITION DID PERIOD:9497.00 HOUR INTEGRATIONRELEASE iojx .. SCALE;1 MODEL: TIME INTEGRATED STRAIGHT LINE START DOSE INTEGRATION; 01/01/03 01;00 END DOSE INTEGRATION: 123S1I63 24:80 CONTOUR D/D LEGEND (1/M2)

I E.aBE-89 1 .0E-09-2.8E-09 7.OE-1 0-1 .OE-B9 4.BE-10-7.SE-18 2.BE-1 0-4.BE-10 1.BE-10-2.eE-10 M.OE-11-1 .eE-10

4. OE-1-7. .E-11 2.EE-11-4.0E-il 17 C - Q

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK) 18

I I I I I I I I I I I Jariuay 1 -YLjuembtr. i, 2dui Docket Nos. 50-317/50-318/72-8 Table 1 Synopsis of 2003 Calvert Cliffs Nuclear Power Plant Radiological Environmental Monitoring Program Sample Type Sampling Number of Number Collected Analysis Analysis Number Analyzed Frequency' Locations Frequency' Aquatic Environment Bay Water MC 2 24 Gamma M 24 H-3 QC 8 Fish2 A 2 4 Gamma A 4 Oysters Q 2 8 Gamma Q 8 Shoreline Sediment SA 1 2 Gamma SA 2 Atmospheric Environment Air Iodine" W 5 255 1-131 W 255 Air Particulates4 W 5 255 Gross Beta W 255 Gamma MC 60 Direct Radiation Ambient Radiation Q 23 546 TLD Q 546 Terrestrial Environment Vegetation 5 M 3 36 Gamma M 36

' 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 hour8.333333e-4 days 0.02 hours 1.190476e-4 weeks 2.7396e-5 months decay. Gamma spectroscopy performed on monthly composites of weekly samples 5 Monthly during growing season 19

January 1 - December 31, 2003 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 Type and Total Lower Limit of Indicator Location with Highest Annual Control Locations Sampled (Unit of Number of Detection Locations Mean Highest Annual Mean (F) / Ranger Mean (F)/Rangel Measurement) Analyses (LLD) (F)/Rangel Mean Performed Name/Distance &

Direction 2 Aquatic Environment Bay Water H-3 (8) 33 380 (4/4) Discharge Vicinity 380 (4/4) 53 (1/4)

(pCi/L) (207-767) Wa2 (207-767) --

0.3 km N Atmospheric Environment Air Particulates Gross Beta (255) 0.5 1.4 (203/203) Route 765 at 1.7 (52/52) 1.4 (52/52) 3 (10-2 pCiMn ) (0.2-3.0) Lusby A4 (0.8-3.0) (0.5-2.2) 2.9 km SSW Direct Radiation Ambient Radiation TLD (546) 12.02 (474/474) Taylors Island 15.96 (24/24) 13.39 (72/72)

(mR/90 days) (9.38-16.01) DR23 (14.49-17.15) (9.95-17.15) 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 I I I I I I I I I I I I I

January I - December 31, 2003 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, six additional canisters of spent fuel were transferred to the ISFSI.

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 and the current and previous CCNPP REMP periods. These comparisons show little deviations from previous periods and are very close to the natural background levels of 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.

21

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 III.B. PROGRAM III.B.1 Obiectives 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,

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. 4).

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.

lI.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. 4). 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).

22

January I - December 31, 2003 Docket Nos. 50-317/50-318/72-8 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 (SFAI), CCNPP Visitor's Center (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 0.3 x 10-2 to 3.4 x 10-2 pCi/m3 for the indicator locations and 0.5 x 10-2 to 2.8 x 10-2 pCi/m 3 for the control location. The location with the highest overall mean of 1.6 x 10-2 pCi/m 3 was SFA1, Met Station.

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 TerrestrialEnvironment 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.

IR.C.2.a Vegetation 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),

NNW of 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.

Cesium- 137 was detected in four quarterly samples from both indicator and control locations.

The Cs-137 concentration ranged from 19 +17 to 59 +25 pCi/kg. This range is consistent with that found to be due to the residual fallout in wind-borne soil dust from past atmospheric nuclear weapons testing. No other 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.

23

January I - December 31, 2003 Docket Nos. 50-317/50-318/72-8 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 twelve quarterly samples from both indicator and control locations. The Cs-137 concentrations ranged from 48 +20 to 547 +73 pCi/kg. While the presence of Cs-137 in 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.

IH.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 SFDRI); 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 SFDR10); WNW of ISFSI, (sample code SFDR1 1); WSW of ISFSI, (sample code SFDR12); South of ISFSI, (sample code SFDR13); 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.

Following up on the correction cited in the Annual Radiological Environmental Operating Report for 2002, dealing with the sector positions of all the sites surrounding the ISFSI, two additional TLD sites were established during the fourth quarter to ensure that ambient radiation levels are measured in all sixteen meteorological sectors. These sites were designated as SFDRI 7 in the NNE sector of the ISFSI and SFDRI8 in the W sector of the ISFSI.

The mean 90 day ambient radiation measured at the ISFSI indicator locations was 25.27 mR and ranged from 9.65 to 68.86 mR as reported in Table 4. The control location showed a 90 day mean of 13.77 mR and ranged from 13.03 to 15.13 mR. A comparison of the mean and ranges of the current TLD data with those of both the historical data and the regional data (22-54, 10) reveals only one set of elevated TLD readings. That location with the highest overall mean of 24

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 47.00 mR with a range of 38.08 to 51.80 mR was SFDR1O, NW of ISFSI. These readings are consistent with those expected from the storage of spent fuel in the ISFSI (Refs. 22-54, 10). 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.

25

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 FIGURE 7 Mean TLD Gamma Dose, ISFSI 9

- Control Location (SFDR7) 8-

-w-- ISFSI Mean (DR7 & 30, SFDR1-6, 8-16) 7-6-

C/U ,--'

V 5-

.-- - ,W' C')

4 E

3-2-

Z2- I

,I I 90 91 92 93 94 95 96 97 98 99 00 01 02 03 26 I I I I I I I I I I I I I t I

I I I January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 Table 3 Synopsis of 2003 Calvert Cliffs Nuclear Power Plant Independent Spent Fuel Storage Installation Radiological Environmental Monitoring Program Sample Type Sampling Number of Locations Number Collected Analysis Analysis Frequency1 Number Analyzed Freauencv' Atmospheric Environment Air Particulatesz W 5 255 Gross Beta W 255 Gamma MC 60 Direct Radiation Ambient Radiation Q 20 438 TLD Q 438 Terrestrial Environment Vegetation Q 5 20 Gamma Q 20 Soil Q 5 20 Gamma Q 20

' W-weekly, M-monthly, Q-quarterly, SA-semiannual, A-annual, C-composite 2 Beta counting is performed after >= 72 hour8.333333e-4 days 0.02 hours 1.190476e-4 weeks 2.7396e-5 months decay. Gamma spectroscopy performed on monthly composites of weekly samples 27

January 1 - December 31, 2003 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 Type and Total Lower Limit Indicator Location with Highest Control Sampled (Unit of Number of of Detection Locations Mean Highest Annual Mean Annual Mean Locations Measurement) Analyses (LLD) (F)/Range' Name/Distance & (F) / Range' Mean Performed Direction 2 (F)/Range' Atmospheric Environment Air Particulates Gross Beta (255) 0.5 1.4 (204/204) MET Station SFA1 1.6 (51/52) 1.5 (51/51)

(10-2 pCi/m 3 ) (0.3-3.4) 0.4 km NW (0.8-3.4) (0.5-2.8)

Direct Radiation Ambient Radiation TLD (438) - 25.27 (414/414) NW of ISFSI SFDR1O 47.00 (24/24) 13.77 (24/24)

(mR/90 days) (9.65-68.86) 0.1 km NW (38.08-51.80) (13.03-15.13)

Terrestrial Environment Vegetation Gamma (20) 27 52 (3/16) On Site before 54 (2/4) 19 (1/4)

(pCi/L) Cs-137 (47-59) Entrance to Camp (49-59) --

Conoy SFb5 0.7 km SE Soil Gamma (20) 17 300 (8/16) NNW of ISFSI SFS3 362 (4/4) 82 (4/4) upo deetal _Ma mesreet only Frcto (F of deetbemaueettseiidloainsidctdiaetee (pCi/kg) ragan bae Cs-137 (89-547) 0.1 km NNW (89-547) (48-114)

' Mean and range based upon detectable measurements only. Fraction (F) of detectable measurements at specified locations is indicated in parentheses 2 From the centerpoint of the ISFSI facility 28 iI I Il I I I

January I - December 31, 2003 Docket Nos. 50-317/50-318/72-8 IV. REFERENCES (1) 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.

(2) Offsite Dose Calculation Manual for the Calvert Cliffs Nuclear Power Plant.

(3) CP-234, Specification and Surveillance for the Radiological Environmental Monitoring Program.

(4) Constellation Energy Laboratory Procedures Manual, General Services Department.

(5) Constellation Energy, "Land Use Survey Around Calvert Cliffs Nuclear Power Plant, August 2003."

(6) Calvert Cliffs Independent Spent Fuel Storage Installation Technical Specifications, Appendix A to Materials License SNM-2505 29

January I - December 31, 2003 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK) 30

January 1 - December 31, 2003 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-I . 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.

31

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK) 32

January I - December 31, 2003 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 ..35 A-2 Locations of Environmental Sampling Stations for the Independent Spent Fuel Storage Installation at Calvert Cliffs ................................................................... 41 Figure Title Page A-I Map of Southern Maryland and Chesapeake Bay Showing Location of Calvert Cliffs Nuclear Power Plant ................................................................... 36 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 33

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK) 34

January 1 - December 31, 2003 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 DRI I 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 DRI9 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 lal,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 la6 Kenwood Beach 10.7 6.6 NNW lalO Hog Island 15.3 9.5 SSE Ibl,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 1Distance and direction from the central point between the two containment buildings.

2 Common to both the REMP and ISFSI monitoring program 35

January I - December 31, 2003 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 36 COS

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 FIGURE A-2 Calvert Cliffs Nuclear Power Plant Sampling Locations 0-2 Miles If

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January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK) 38

January 1- December 31, 2003 Docket Nos. 50-317/50-318/72-8 FIGURE A-3 Calvert Cliffs Nuclear Power Plant Sampling Locations 0-10 Miles MIMI lime".

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January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK) 40

January 1 - December 31, 2003 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 A___2 _On Site before Entrance to Camp Conoy 0.3 ESE SFAI Meteorological Station 0.3 NW SFA2 CCNPP Visitor's Center 0.8 N SFA3 NNW of ISFSI 0.1 NNW SFA4 SSE of ISFSI 0.1 SSE Direct Radiation SFDRl 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 SFDR10 NW of ISFSI 0.1 NW SFDRI I WNW of ISFSI 0.1 WNW SFDR12 WSW of ISFSI 0.04 WSW SFDR13 South of ISFSI 0.11 SFDR14 SE of ISFSI 0.1 SE SFDR15 ENE of ISFSI 0.1 ENE SFDR16 SSW of ISFSI 0.04 SSW SFDR17 NNE of ISFSI 0.1 NNE SFDR18 West of ISFSI 0.04 W DR72 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 SFSI 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, 2003 Docket Nos. 50-317/50-318/72-8 FIGURE A-4 Independent Spent Fuel Storage Installation Sampling Locations SW SSW I- - ,,

r 42 C, (I

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 FIGURE A-5 Enlarged Map of the Independent Spent Fuel Storage Installation Sampling Locations

~~~NNW NNW /4 E idE .

1W : ENE At

-SSb4 SFS; 43 ( )

January 1 - December 31, 2003 L Docket Nos. 50-317/50-318/72-8 L

L II U

(LEFT BLANK)

U L

L 44

January I - December 31, 2003 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, 2003 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK) 46

January I - December 31, 2003 Docket Nos. 50-317/50-318/72-8 TABLE OF CONTENTS - ANALYTICAL RESULTS Analysis Results for the REMP and the ISFSI Table Title Page B-1 Concentration of Tritium and Gamma Emitters in Bay Water .48 B-2 Concentration of Gamma Emitters in the Flesh of Edible Fish .49 B-3 Concentration of Gamma Emitters in Oyster Samples .50 B-4 Concentration of Gamma Emitters in Shoreline Sediment .51 B-5 Concentration ofIodine-131 in Filtered Air .52 B-6 Concentration of Beta Emitters in Air Particulates .54 B-7 Concentration of Gamma Emitters in Air Particulates .58 B-8a Concentration of Gamma Emitters in Vegetation Samples ..................................................... 59 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 ..................................................................... 63 B-1l Typical LLDs for Gamma Spectrometry ..................................................................... 64 B-12 Direct Radiation ..................................................................... 65 47

January 1 - December 31, 2003 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 +/- 2a)

Sample Code Sample H-3' Gamma Emitters Date Wal 1/31/2003

Intake Vicinity 2/28/2003

3/28/2003 3/31/2003 <38 4/30/2003

5/28/2003

6/27/2003

6/30/2003 <40 8/4/2003

9/4/2003

9/28/2003

9/30/2003 53 +/- 39 11/8/2003 12/5/2003 12/31/2003 <43 Wa2 1/31/2003

Discharge Vicinity 2/28/2003

3/28/2003

3/31/2003 767 +/- 44 4/30/2003 5/28/2003 6/27/2003

6/30/2003 272 +/- 41 814/2003 9/4/2003

9/28/2003

9/30/2003 207 +/- 41 11/8/2003 12/5/2003 12/31/2003 275 +/- 43

1Quarterly composite of monthly samples

All Non-Natural Gamma Emitters <MDA 48

January I - December 31, 2003 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 Co,de Sample Date Sample Type GEimma Emitters la1 7/28/2003 Striped bass Discharge Area Ia2 7/28/2003 Croaker Discharge Area Ia4 7/28/2003 Croaker Patuxent River Ia5' 7128/2003 Striped bass Patuxent River

' Control Location

All Non-Natural Gamma Emitters <MDA 49

January 1 - December 31, 2003 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 3/20/2003

Camp Conoy 6/24/2003

8/14/2003

10/21/2003

la6' 3/20/2003

Kenwood Beach 6/24/2003

8/14/2003

10/21/2003

' Control Location

All Non-Natural Gamma Emitters <MDA 50

January 1 - December 31, 2003 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 WbI 06/05/2003 1 Shoreline at Barge Rd. 12115/2003 1

'All Non-Natural Gamma Emitters <MDA 51

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 Table B-5 Concentration of Iodine-131 in Filtered Air (Results in units of 1O 3 pCi/m3 + 2ta)

Start Date Stop Date Al A2 A3 A4 A5I Entrance to Camp Conoy Bay Breeze Route 765 at EOF Camp Conoy Siren Rd Lusby 12/30/2002 1/6/2003 * * * *

1/6/2003 1/13/2003 * * * *

1/13/2003 1/20/2003 * * *

1/20/2003 1/27/2003 * * * *

1/27/2003 2/3/2003 * * * *

2/3/2003 2/10/2003 * * * *

2/10/2003 2/19/2003 * * * *

2/19/2003 2/24/2003 ' * * *

2/24/2003 3/3/2003 * * * *

3/3/2003 3/10/2003 * * * *

3/10/2003 3/17/2003 * * * *

3/17/2003 3/24/2003 * * * *

3/24/2003 3/31/2003 * * * *

3/31/2003 4/7/2003 * * * *

4/7/2003 4/14/2003 * * * *

4/14/2003 4/21/2003 * * * *

4/21/2003 4/28/2003 * * * *

4/28/2003 5/5/2003 * * * *

5/5/2003 5/12/2003 * * * *

5/12/2003 5/19/2003 * * * *

5/19/2003 5/26/2003 * * * *

5/26/2003 6/2/2003 * * * *

6/2/2003 6/9/2003 * * * *

6/9/2003 6/16/2003 * * *

6/16/2003 6/23/2003 * * * *

6/23/2003 6/30/2003 * * * *

6/30/2003 7/7/2003 * * * *

7/7/2003 7/14/2003 * * * *

7/14/2003 7/21/2003 * * * *

7/21/2003 7/28/2003 * * * *

7128/2003 8/4/2003 * * * *

8/4/2003 8/11/2003 * * * *

8/11/2003 8/18/2003 * * * *

8/18/2003 8/25/2003 * * * *

8/25/2003 9/1/2003 * * * * *

' Control Location 2 Sampler malfumction/loss of power

<MDA 52

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 Table B Continued Concentration of Iodine-131 in Filtered Air (Results in units of 10-3 pCi/M3 +/- 2ca)

Start Date Stop D;ate Al A2 A3 A4 A51 Entrance to Camp Conoy Bay Breeze Route 765 at EOF Camp Conoy Siren Rd Lusby 9/1/2003 9/8/2003 * * *

9/8/2003 9115/2003 * * * *

9/15/2003 9/22/2003 2

2 *

9/22/2003 9/29/2003 * * * *

9129/2003 10/6/2003 * * * *

10/6/2003 10/13/2003 * * * *

10/13/2003 10/20/2003 * * * *

10/20/2003 10/27/2003 * * * *

10/27/2003 11/3/2003 * * * *

11/3/2003 11/10/2003 * * * *

11/10/2003 11/17/2003 * * * *

11/17/2003 11/24/2003 * * * *

11/24/2003 12/1/2003 * * * *

12/1/2003 12/8/2003 * * * *

12/812003 12/15/2003 * * * *

12/15/2003 12/22/2003 * * * *

12(22/2003 12/29/2003 * * * * *

' Control Location 2 Sampler mnalfunction/loss of power

<MDA 53

January I - December 31, 2003 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 + 2a)

Start Date Stop Date Al A2 A3 A4 A5' Entrance to Camp Conoy Bay Breeze Route 765 at EOF Camp Conoy Siren Rd Lusby

_ _ . _ _ . =

12/30/2002 1/6/2003 1.1 +/-0.2 1.0 +/- 0.2 0.9 +/- 0.2 1.3 +/- 0.2 1.0 +/- 0.2 1/6/2003 1/13/2003 2.0 +/- 0.2 1.4 +/- 0.2 1.3 +/- 0.2 1.9 +/- 0.2 1.7 +/- 0.2 1/13/2003 1/20/2003 2.4 +/- 0.2 1.6 +/- 0.2 2.0 +/- 0.2 2.3 +/- 0.2 1.7 +/- 0.2 1/20/2003 1/27/2003 2.0 +/- 0.2 1.4+/- 0.2 1.8 +/- 0.2 1.8 +/- 0.2 1.7 +/- 0.2 1/27/2003 2/3/2003 1.5+/- 0.2 1.0 +/- 0.2 1.1 +/-0.2 2.0 +/- 0.2 1.2 +/- 0.2 2/3/2003 2/10/2003 2.0 +/- 0.2 1.3 +/- 0.2 1.4 +/- 0.2 2.4 +/- 0.2 1.6 +/- 0.2 2/10/2003 2/19/2003 1.7 +/- 0.2 1.0 +/- 0.1 1.5 +/- 0.2 1.6 +/- 0.2 1.4 +/-i0.2 2/19/2003 2/24/2003 0.8 +/- 0.2 1.3 +/- 0.3 1.7 +/- 0.3 1.0 +/- 0.2 2/24/2003 3/3/2003 1.4 +/- 0.2 1.0 +/- 0.2 1.4 +/- 0.2 2.0 +/- 0.2 1.1 +/- 0.2 3/3/2003 3/10/2003 1.8 +/- 0.2 1.2 +/- 0.2 1.4 +/- 0.2 2.0 +/- 0.2 1.5 +/- 0.2 3/10/2003 3/17/2003 2.1 +/- 0.2 1.3 +/- 0.2 1.5 +/- 0.2 2.2 +/- 0.2 2.0 +/- 0.2 3/17/2003 3/24/2003 1.4 +/- 0.2 0.8 +/- 0.2 0.9 +/- 0.2 1.4 +/- 0.2 1.4 +/- 0.2 3/24/2003 3/31/2003 1.1 +/- 0.2 0.9 +/- 0.2 1.6 +/- 0.2 1.4 +/- 0.2 1.3 +/- 0.2 3/31/2003 4/7/2003 1.2 +/- 0.2 1.1 +/- 0.2 1.2 +/- 0.2 1.6 +/- 0.2 1.4 +/- 0.2 4/7/2003 4/14/2003 0.5 +/- 0.2 0.8 +/- 0.2 0.8 +/- 0.2 1.0 +/- 0.2 1.0 +/- 0.2 4/14/2003 4/21/2003 1.6 +/- 0.2 1.4 +/- 0.2 2.0 +/- 0.3 2.1 +/- 0.2 1.8 +/- 0.2 4/21/2003 4/28/2003 1.3 +/- 0.2 0.8 +/- 0.2 1.0 +/- 0.2 1.3 +/- 0.2 1.1 +/- 0.2 4/28/2003 5/5/2003 1.3 +/- 0.2 0.9 +/- 0.3 1.3 +/- 0.2 1.8 +/- 0.2 1.2 +/- 0.2 5/5/2003 5/12/2003 0.9 +/- 0.1 0.9 +/- 0.2 0.7 +/- 0.1 1.2 +/- 0.2 0.9 +/- 0.2 5/12/2003 5/19/2003 0.6 +/- 0.1 0.9 +/- 0.2 0.5 +/- 0.1 1.0 +/- 0.2 0.5 +/- 0.1 5/19/2003 5/26/2003 0.7 +/- 0.1 0.8 +/- 0.2 0.7 +/- 0.1 0.9 +/- 0.2 0.8 +/- 0.2 5/26/2003 6/2/2003 0.9 +/- 0.1 0.9 +/- 0.2 0.8+/- 0.2 1.1 +/- 0.2 0.9+/- 0.2 6/2/2003 6/9/2003 0.6 +/- 0.2 0.7 +/- 0.2 0.6 +/- 0.2 1.1 +/- 0.2 1.0 +/- 0.2 6/9/2003 6/16/2003 1.0 +/- 0.2 0.7 +/- 0.2 1.3 +/- 0.2 1.2 +/- 0.2 6/16/2003 6/23/2003 0.6 +/- 0.2 0.4 +/- 0.1 0.4 +/- 0.2 0.8 +/- 0.2 0.5 +/- 0.2 6/23/2003 6/30/2003 1.3 +/- 0.2 0.6 +/- 0.2 1.0 +/- 0.2 2.3 +/- 0.2 1.3 +/- 0.2 6/30/2003 7/7/2003 1.0 +/- 0.2 0.5 +/- 0.2 0.8 +/- 0.2 2.2 +/- 0.2 1.3 +/- 0.2 7/7/2003 7/14/2003 0.5 +/- 0.2 0.2 +/- 0.0 0.8 +/- 0.2 1.3 +/- 0.2 0.8 +/- 0.2 7/14/2003 7/21/2003 0.9 +/- 0.2 0.3 +/- 0.0 0.7 +/- 0.2 1.5 +/- 0.2 1.6 +/- 0.2 7/21/2003 7/28/2003 1.0 +/- 0.2 0.7 +/- 0.2 0.9 +/- 0.2 1.6 +/- 0.2 1.5 +/- 0.2 7/28/2003 8/4/2003 1.0 +/- 0.2 0.6 +/- 0.2 0.8 +/- 0.2 1.4 +/- 0.2 0.9 +/- 0.2 8/4/2003 8/11/2003 0.8 +/- 0.2 0.8 +/- 0.2 1.0 +/- 0.2 1.2 +/- 0.2 1.4 +/- 0.2 8/11/2003 8/18/2003 1.1 +/- 0.2 0.4 +/- 0.2 0.8+/- 0.2 1.1 +/- 0.2 1.4 +/-0.2 8/18/2003 8/25/2003 1.1 +/- 0.2 0.7 +/- 0.2 1.2 +/- 0.2 1.5 +/- 0.2 1.4 +/- 0.2 8/25/2003 9/1/2003 1.2 +/- 0.2 0.6 +/- 0.2 1.2 +/- 0.2 1.8 +/- 0.2 1.5 +/- 0.2

' Control Location 2 Sampler malfunction/loss of power 54

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 Table B Continued Concentration of Beta Emitters in Air Particulates (Results in units of 10-2 pCi/m 3 +/- 2a)

Start Date Stop Date Al A2 A3 A4 A51 Entrance to Camp Conoy Bay Breeze Route 765 at EOF Camp Conoy Siren Rd Lusby 9/1/2003 9/8/2003 2 0.6 +/- 0.2 1.3 +/- 0.2 1.5 +/- 0.2 1.6 +/- 0.2 9/8/2003 9/15/2003 1.2 0.2 0.6 +/- 0.2 0.7 +/- 0.2 1.4 +/- 0.3 1.3 +/- 0.2 9/15/2003 9/22/2003 2 1.5 +/- 0.3 2 1.6 +/- 0.3 1.3 +/- 0.2 9/22/2003 9/29/2003 2.2 +/- 0.2 1.9 +/- 0.2 2.2 +/- 0.3 2.3 +/- 0.2 1.7 +/- 0.2 9/29/2003 10/6/2003 1.3 +/- 0.2 1.0 +/- 0.2 0.9 +/- 0.2 1.3 +/- 0.2 1.0 +/- 0.2 10/6/2003 10/13/2003 3.0 +/- 0.2 2.8 +/- 0.2 2.1 +/- 0.2 3.0 +/- 0.2 2.0 +/- 0.2 10/13/2003 10/20/2003 1.7 +/- 0.2 1.6 +/- 0.2 1.3 +/- 0.2 1.9 +/- 0.2 2.0 +/- 0.2 10/20/2003 10/27/2003 1.4 +/- 0.2 1.9 +/- 0.2 1.4 +/- 0.2 1.4 +/- 0.2 1.0 +/- 0.2 10/27/2003 11/3/2003 2.0 +/- 0.2 2.1 +/- 0.2 1.7 +/- 0.2 2.3 +/- 0.2 1.6 +/- 0.2 11/3/2003 11/10/2003 1.5+/- 0.2 1.6+/- 0.2 1.0 +/- 0.1 1.5+/- 0.2 1.1 +/- 0.2 11/10/2003 11/17/2003 2.0 +/- 0.2 1.9 +/- 0.2 1.4 +/- 0.2 1.7 +/- 0.2 1.2 +/- 0.2 11/17/2003 11/24/2003 2.1 +/- 0.2 2.5 +/- 0.3 1.9 +/- 0.2 2.8 +/- 0.3 2.2 +/- 0.2 11/24/2003 12/1/2003 1.7 +/- 0.2 2.1 +/- 0.3 1.4 +/- 0.1 1.9 +/- 0.2 1.8 +/- 0.2 12/11/2003 12/8/2003 1.2 +/- 0.2 1.3 +/- 0.2 1.1 +/- 0.2 1.5 +/- 0.2 1.2 +/- 0.2 12/8/2003 12/15/2003 1.3 +/- 0.2 1.4 +/- 0.2 0.9 +/- 0.1 1.3 +/- 0.2 1.6 +/- 0.2 12/15/2003 12/2212003 2.1 +/- 0.2 2.2 +/- 0.2 1.8 +/- 0.2 2.2 +/- 0.2 2.2 +/- 0.2 12/22/2003 12/29/2003 2.0 +/-0.2 2.1 +/-0.2 1.6 +/- 0.2 2.1 +/- 0.2 2.1 +/- 0.2

' Control Location 2Sampler malfunction/loss of power 55

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 Table B Continued Concentration of Beta Emitters in Air Particulates (Results in units of 10-2 pCi/m 3 I 2a)

Start Date Stop Date SFA1 SFA21 SFA3 SFA4 MET Station Visitors Center NNW of ISFSI SSE of ISFSI 12/30/2002 1/6/2003 1.5 +/- 0.2 1.3+/-0.2 1.3+/- 0.2 1.2 +/- 0.2 1/6/2003 1/13/2003 2.4 +/- 0.3 2.0 +/- 0.2 2.0 +/- 0.2 1.8 +/- 0.2 1/13/2003 1/20/2003 2.6 +/- 0.3 2.3 +/- 0.2 2.2 +/- 0.2 2.2 +/- 0.2 1/20/2003 1/27/2003 2.4 +/- 0.3 2.1 +/- 0.2 1.9 +/- 0.2 1.9 +/- 0.2 1/27/2003 2/3/2003 2.2 +/- 0.2 1.9+/- 0.2 1.6 +/- 0.2 1.4 +/- 0.2 2/3/2003 2/10/2003 2.3 +/- 0.3 2.0 +/- 0.2 1.9 +/- 0.2 1.8 +/- 0.2 2/10/2003 2/19/2003 1.5 +/- 0.2 1.4 +/- 0.2 1.2 +/- 0.1 1.0 +/- 0.1 2/19/2003 2/24/2003 1.4 +/- 0.3 1.4 +/- 0.3 1.4 +/- 0.2 1.3 +/- 0.2 2/24/2003 3/3/2003 2.0 +/- 0.2 2.0 +/- 0.2 1.4 +/- 0.2 1.6 +/- 0.2 3/3/2003 3/10/2003 2.4 +/- 0.2 2.3 +/- 0.2 1.8 +/- 0.2 2.1 +/- 0.2 3/1012003 3117/2003 2.3+/-0.2 2.1 +/-0.2 2.1 +/-0.2 1.6+/-0.2 3/17/2003 3/24/2003 1.5 +/- 0.2 1.5 +/- 0.2 1.6 +/- 0.2 1.1 +/- 0.2 3/24/2003 3/31/2003 1.3 +/- 0.2 1.5 +/- 0.2 1.2 +/- 0.2 1.0 +/- 0.2 3/31/2003 4/7/2003 1.3 +/- 0.2 1.3 +/- 0.2 1.7 +/- 0.2 1.1 +/- 0.2 4/7/2003 4/14/2003 1.1 +/- 0.2 1.3 +/- 0.2 0.9 +/- 0.2 1.0 +/- 0.2 4/14/2003 4/21/2003 2.4 +/- 0.3 1.8 +/- 0.2 1.9 +/- 0.2 1.7 +/- 0.2 4/21/2003 4/28/2003 1.4 +/- 0.2 1.1 +/- 0.2 1.1 +/- 0.2 0.8 +/- 0.1 4/28/2003 5/5/2003 2.3 +/- 0.3 1.5 +/- 0.2 1.7 +/- 0.2 1.1 +/- 0.2 5/512003 5/12/2003 0.9 i 0.2 0.9 +/- 0.2 1.1 +/- 0.2 0.7 +/- 0.2 5/12/2003 5/19/2003 0.9 +/- 0.2 1.0 +/- 0.2 1.0 +/- 0.2 0.5 +/- 0.2 5/19/2003 5/26/2003 0.8 +/- 0.2 0.9 +/- 0.1 0.9 +/- 0.2 0.8 +/- 0.2 5/26/2003 6/2/2003 1.0+/- 0.2 1.1 +/- 0.2 1.1 +/- 0.2 0.7+/- 0.1 6/2/2003 6/9/2003 0.9 +/- 0.2 0.8 +/- 0.2 1.0 +/- 0.2 0.7 +/- 0.2 6/9/2003 6/16/2003 1.1 +/-0.2 1.1 +/-0.2 1.3+/-0.2 0.8 +/-0.1 6116/2003 6123/2003 0.8 +/- 0.2 0.7 +/- 0.2 0.8 +/- 0.2 0.3 +/- 0.1 6/23/2003 6/30/2003 2.2 +/- 0.2 1.6+/- 0.2 1.8 +/- 0.2 0.8 +/- 0.2 6/30/2003 7/7/2003 1.7 +/- 0.2 1.6 +/- 0.2 1.5 +/- 0.2 0.6 +/- 0.2 7/7/2003 7/14/2003 1.4 +/- 0.2 1.0 +/- 0.2 0.9 +/- 0.2 0.8 +/- 0.2 7/14/2003 7/21/2003 1.6 +/- 0.2 1.4 +/- 0.2 1.6 +/- 0.2 0.6 +/- 0.2 7/21/2003 7/28/2003 1.8 +/- 0.2 1.7 +/- 0.2 1.9 +/- 0.2 0.7 +/- 0.2 7/28/2003 8/4/2003 0.8 +/- 0.2 1.0 +/- 0.2 1.0 +/- 0.2 0.7 +/- 0.2 8/4/2003 8/11/2003 1.0 +/- 0.2 0.8 +/- 0.1 1.3 +/- 0.2 0.6 +/- 0.2 8/11/2003 8118/2003 1.5 +/- 0.2 1.0 +/- 0.2 1.6 +/- 0.2 0.5 +/- 0.2 8/18/2003 8/25/2003 1.9 +/- 0.2 2.1 +/- 0.2 1.9 +/- 0.2 0.9 +/- 0.2 8125/2003 911/2003 1.7 +/- 0.2 2.1 +/- 0.2 1.7 +/- 0.2 1.0 +/- 0.2

' Control Location 56

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 Table B Continued Concentration of Beta Emitters in Air Particulates (Results in units of 10-2 pCi/m3 +/- 2a)

Start Date Stop Date SFA1 SFA2' SFA3 SFA4 MET Station Visitors Center NNW of ISFSI SSE of ISFSI 9/1/2003 918/2003 1.6 +/- 0.2 1.3 +/- 0.2 1.2 +/- 0.2 1.3 +/- 0.2 9/812003 9/1512003 1.2 +/- 0.3 0.5 +/- 0.2 0.7 +/- 0.2 0.8 +/- 0.2 9/15/2003 9/22/2003 1.3 +/- 0.2 1.7 +/- 0.2 1.7 +/- 0.2 0.7 +/- 0.2 9/2212003 9/2912003 2.5 +/- 0.2 2.1 +/-0.2 2.4 +/-0.2 0.9 +/- 0.2 9/29/2003 10/6/2003 1.4 +/-0.2 1.3 +/- 0.2 1.4 +/- 0.2 1.0 +/- 0.2 10/6/2003 10/13/2003 3.4 +/- 0.3 2.8 +/- 0.2 2.2 +/- 0.2 1.9 +/- 0.2 10/1312003 10/20/2003 1.8 +/- 0.2 2.1 +/-0.2 2.5 +/- 0.2 1.5 +/- 0.2 10/20/2003 10/27/2003 1.1 +/- 0.2 1.0 +/- 0.2 1.6 +/- 0.2 1.3 +/- 0.2 10/27/2003 11/3/2003 2.1 +/-0.2 2.1 +/-0.2 2.1 +/-0.2 1.9 +/- 0.2 11/3/2003 11/10/2003 1.1 +/-0.2 1.4 +/-0.2 1.3+/- 0.2 1.2 +/- 0.2 11/10/2003 11/17/2003 1.6 +/- 0.2 1.8 +/- 0.2 1.7 +/- 0.2 1.1 +/- 0.2 11/17/2003 11/24/2003 2 2.5+/- 0.2 2.1 +/- 0.2 2.3+/- 0.2 11/24/2003 12/1/2003 1.9 +/- 0.2 1.7 +/- 0.2 1.9 +/- 0.2 1.6 +/- 0.2 12/1/2003 12/8/2003 1.2 +/- 0.2 1.2 +/- 0.2 1.3 +/- 0.2 1.2 +/- 0.2 12/8/2003 12/15/2003 1.0 +/- 0.2 1.5 +/- 0.2 1.0 +/- 0.2 0.9 +/- 0.2 12/15/2003 12/22/2003 2.0 +/- 0.2 1.9 +/- 0.2 1.7 +/- 0.2 12/22/2003 12/29/2003 1.9 +/- 0.2 2.2 +/- 0.2 2.1 +/- 0.2 1.9 +/- 0.2

' Control Location 2 Sampler ralfunction/loss of power 57

January 1 - December 31, 2003 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/m3 +/- 2cr)

Sample Al A2 A3 A4 A51 Date Entrance to Camp Conoy Bay Breeze Rd Route 765 at EOF CamD Conov Siren Lusbv 1/15/2003 * * * *

2/15/2003 * * * *

3/15/2003 * * * *

4115/2003 * * * *

5/15/2003 * * * *

6/15/2003 * * * *

7/15/2003 * * * *

8/15/2003 *

9/15/2003 * * * *

10/15/2003 *

11/15/2003 * * * *

12/15/2003 *

Sample SFAI SFA2 SFA3 SFA4 Date MET Station Visitors Center NNW of ISFSI SSE of ISFSI 1/15/2003 * * *

2/15/2003 *

3/15/2003 * * *

4/15/2003 * * *

5/15/2003

6/15/2003 * * *

7/15/2003 * * *

8/15/2003 * * *

9/15/2003 * * *

10/15/2003 * * *

11/15/2003 * * *

12/15/2003 * *

' Control Location

AlI Non-Natural Ganmma Ernitters <MDA 58

January 1 - December 31, 2003 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 Sample Type Gamma Emitters Date Ib1 7/28/2003 Collards Bay Breeze Rd 8/25/2003 Collards 9129/2003 Collards 11/3/2003 Collards Ib2 7/28/2003 Cabbage

Bay Breeze Rd 8/25/2003 Cabbage

9/29/2003 Cabbage

11/3/2003 Cabbage

Ib3 7/28/2003 Broccoli

Bay Breeze Rd 8/25/2003 Brussels sprouts 9/29/2003 Brussels sprouts

11/3/2003 Brussels sprouts

Ib4 7/28/2003 Collards

Camp Conoy Entrance 8/25/2003 Collards

9/29/2003 Collards

11/3/2003 Collards

lb5 7/28/2003 Cabbage

Camp Conoy Entrance 8/25/2003 Cabbage

9/29/2003 Cabbage

11/312003 Cabbage

1b6 7/28/2003 Broccoli

Camp Conoy Entrance 8/25/2003 Brussels sprouts

9/29/2003 Brussels sprouts

11/3/2003 Brussels sprouts 1b7 1 7/28/2003 Collards

EOF 8/25/2003 Collards

9/29/2003 Collards

11/3/2003 Collards

1b8' 7/28/2003 Cabbage

EOF 8/25/2003 Cabbage

9/29/2003 Cabbage

11/3/2003 Cabbage

1Control Location

AII Non-Natural Garmma Emitters <MDA 59

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 Table B-8a - Continued Concentration of Gamma Emitters in Vegetation Samples (Results in units of pCi/kg (wet) + 2cr)

Sample Code Sample Sample Type Gamma Emitters Date 1b9' 7/28/2003 Broccoli

EOF 8/25/2003 Brussels sprouts

9/29/2003 Brussels sprouts

11/3/2003 Brussels sprouts *

' Control Location

AIl Non-Natural Ganmma Ernitters <MDA 60

January I - December 31, 2003 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 Cs-137 Gamma Emitters Date SFb1 3/24/2003 MET Station 6/16/2003 1 9/15/2003

1 12/8/2003 SFb2 2 3/24/2003 19 +/- 17

Visitor's Center 6/16/2003 1

9/15/2003 1

12/8/2003

SFb3 3/24/2003 1

NNW of ISFSI 6/16/2003 '

9/15/2003 '

12/8/2003 47 +/- 36

SFb4 3/24/2003 '

SSE of ISFSI 6/16/2003 '

9/15/2003 1 12/812003 '

SFb5 3/24/2003 49 +/- 19

On Site before Entrance 6/16/2003 '

to Camp Conoy 9/15/2003 1218/2003 59 +/-25 *

' This Isotope <MDA 2

Control Location

All Other Non-Natural Gamma Emitters <MDA 61

January 1 - December 31, 2003 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) +/- 2s)

Sample Code Sample Cs-137 Gamma Emitters Date SFS1 3/24/2003

I MET station 6/16/2003 9/15/2003 1

12/8/2003 SFS22 3/24/2003 114+/- 30

Visitors Center 6/16/2003 86 +/- 40

9/15/2003 80+/- 32

12/8/2003 48+/- 20

SFS3 3/24/2003 416 49

NNW of ISFSI 6/16/2003 396 67

9/15/2003 547 73

12/8/2003 89 31

SFS4 3/24/2003 1

SSE of ISFSI 6/16/2003 '

9/15/2003 1

12/8/2003 SFS5 3/24/2003 132 i 28

Entrance to Camp 6/16/2003 337 +/- 39

Conoy 9/15/2003 201 +/-31

12/8/2003 282 35 *

' This Isotope <MDA 2 Control Location

All Other Non-Natural Gamma Emitters <MDA 62

I

( I I I I JanL-, 1- L-mbL ,,20L, Docket Nos. 50-317/50-318/72-8 TABLE B-10 Typical MDA Ranges for Gamma Spectrometry Selected Bay Water Fish Shellfish Shoreline Vegetation Soil Particulates Nuclides pCi/l pCi/kg pCi/kg pCi/kg pCi/kg pCi/kg 10-3 pCi/m 3 Na-22 1.6 - 3.8 21 - 29 18 - 30 28 - 29 16 - 37 33 - 95 1.3 - 3.4 Cr-51 12-40 160- 166 118 - 176 208 -213 14- 164 203-486 13-39 Mn-54 1.4-3.2 16-20 15-22 26-30 13-28 32-81 1.2-6.2 Co-58 1.5 - 4.0 20 - 23 16 - 26 28 - 32 13 - 26 28 - 79 1.4 - 3.4 Fe-59 3.5 - 11 53 - 74 36 - 65 60 - 77 28 - 69 65 - 174 3.7 - 8.2 Co-60 1.5 - 3.7 18 - 25 18 - 26 27 - 39 15 - 35 23 - 97 1.3 - 3.3 Zn-65 3.3 - 7.9 46 - 62 36 - 57 69 - 97 32 - 73 67 - 238 3.0 - 6.9 Nb-95 1.7 - 5.8 25 - 31 20 - 35 34 - 40 13 - 27 34 - 93 2.1 - 5.0 Zr-95 2.8-6.9 35-44 29-43 45-62 21 -48 53- 141 2.1 -6.4 Ru-106 12-26 131-149 124- 185 224-287 108-239 264-643 10-25 Ag-1Orm 1.2-2.9 15-18 15-18 21-31 11-25 29-88 0.1-2.6 Te-129m 18 - 60 247 - 280 192 - 284 321 - 367 135 - 281 346 - 855 19 - 55 1-131 2.4-49 99 - 121 30-89 50-52 11 -37 32.7- 179 1 Cs-134 1.2 - 2.6 14 - 17 13 - 19 24 - 34.5 11 - 24 27 - 94 1.0 - 2.4 Cs-137 1.2 - 3.0 15 - 18 15 - 34 25 - 30 1.5 - 26 27 - 72 1.0 - 2.8 Ba-140 7.3 - 66 174 - 208 75 - 184 138 - 150 41 - 109 112 - 430 12 - 84 La-140 3.2 - 29 - 49 - 74 75 - 75 17 - 51 60 - 138 8.7 - 19 Ce-144 7.1 - 12 45 - 49 42 - 49 101 - 111 49 - 86 110 - 245 2.8 - 8.2 The MDA range for I-13 1 on a silver zeolite cartridge is typically 4.16 x10-3 to 3.40 x 10-2 63

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 TABLE B-1 1 Typical LLDs for Gamma Spectrometry Precipitation Vegetation Soil Well Water Selected Bay Water Fish Shellfish Sediment Particulate Precipitation Vegetation Soil Well Water Nuclides pCi/I pCi/kg pCi/kg pCi/kg 1° 3 pCi/m 3 pCi/I pCi/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-1 06 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-1 34 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

TheLLD for 1-131 measured on a silver zeolite cartridge is 2.0 x10- 3 pCi/m3 64 I I I I I II I I I f I

I I I I I I I Jaluaryl- lvecember, 2dA03 Docket Nos. 50-317/50-318/72-8 Table B-12 Direct Radiation (Results in Units of mR/90 days -2cr)

Site Code Location First Quarter Second Quarter Third Quarter Fourth Quarter DR01 On Site, along Cliffs 14.42 +/- 0.90 13.86i 1.12 12.46 +/- 2.06 14.09 +/- 3.72 DR02 Route 765, Auto Dump 11.39 +/- 0.70 10.69 +/- 0.55 10.02 +/- 0.81 10.64 +/- 1.18 DR03 Route 765, Giovanni's Tavern 12.07 +/- 0.20 11.63 +/- 0.75 9.96 +/- 0.23 10.70 +/- 0.75 DR04 Route 765, across from White Sands Drive. 13.90 +/- 0.79 13.29 +/- 1.10 11.88 +/- 1.13 12.56 +/- 0.57 DR05 Route 765, St. John's Creek 13.19 +/- 1.11 12.71 +/- 1.03 11.62 +/- 0.75 12.26 +/- 1.17 DR06 Route 765 at Lusby 11.19 +/- 1.01 10.72 +/- 0.32 9.88 +/- 1.43 10.65 +/- 0.85 DR07 Entrance to Camp Conoy 10.91 +/- 0.17 11.06 +/- 0.79 9.65 +/- 1.03 10.18 +/- 0.85 DR08 Camp Conoy Rd at Emergency Siren 16.01 +/- 0.36 15.42 +/- 0.89 14.39 +/- 0.23 15.41 +/- 0.78 DR09 Bay Breeze Rd 12.39 +/- 1.24 12.13 +/- 1.04 11.11 +/- 0.75 11.58 +/- 1.16 DR10 Decatur St. and Calvert Beach Rd. 11.53 +/- 1.45 11.30 +/- 0.53 10.34 +/- 0.64 11.00 +/- 0.56 DR1 Dirt road off Mackall & Parren Rd 12.12 +/- 1.54 11.69 +/- 0.98 10.84 +/- 1.02 11.07 +/- 0.88 DR12 Mackall & Bowen Rds 11.72 +/- 1.21 11.89 +/- 1.33 10.72 +/- 0.62 11.29 +/- 0.86 DRI 3 Mackall Rd, near Waliville 12.93 +/- 0.77 12.65+/- 1.43 11.06+/- 0.96 12.55 +/- 1.19 DR14 Rodney Point 14.53 +/- 0.68 14.38+/- 0.93 13.10 +/- 0.70 DR1 5 Mill Bridge & Turner Rds 13.27 +/- 0.98 12.27 +/- 0.70 11.55 +/- 1.27 11.80 +/- 0.87

' TLD Missing 65

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 Table B-12 Direct Radiation (Results in Units of mRI90 days +/- 2a)

DR16 Across from Appeal School 12.30+/- 1.31 11.77 +/- 0.65 10.25+/- 2.45 10.91 +/- 1.10 DR17 Cove Point & Little Cove Point Rds 13.68 +/- 0.69 13.92+/- 0.95 12.59+/- 1.51 12.88 +/- 0.63 DR18 Cove Point 10.27 0.78 10.35+/- 0.96 9.38 +/- 0.83 10.14 +/- 0.87 DR19 Long Beach 11.81 +/- 0.75 11.94+/- 1.49 10.64+/- 1.93 11.02 +/- 0.79 DR20 On site, near Shore 14.18 1.54 14.01 +/- 0.73 12.59+/- 1.02 13.25 +/- 0.97 DR21 EOF 12.94i 0.20 13.25 +/- 0.53 9.95 1.41 12.71 +/- 1.07 DR22 Solomons Island 12.13 0.58 11.87 +/- 0.33 13.19+/- 0.24 10.80 +/- 0.55 DR23 Taylors Island 16.33 0.53 17.15+/- 2.45 14.49+/- 1.93 15.86 +/- 1.47 DR30 MET Station 13.40+/- 0.46 13.38+/- 1.36 12.27+/- 0.98 12.64 +/- 1.53 SFDR01 SW of ISFSI 17.88+/- 1.16 18.46 +/- 1.42 17.12+/- 2.75 16.21 +/- 1.44 SFDR02 NNW of ISFSI 68.86 +/- 2.74 23.63+/- 1.67 20.84+/- 4.56 23.53 +/- 2.95 SFDR03 North of ISFSI 33.94 +/- 7.53 33.39 +/- 1.64 28.60+/- 9.19 31.25 +/- 6.41 SFDR04 NE of ISFSI 22.66 +/- 2.44 15.15+/- 3.64 23.37 +/- 3.34 SFDR05 East of ISFSI 17.34+/- 2.78 17.54 +/- 2.70 16.60 3.31 16.90 +/- 1.41 SFDR06 ESE of ISFSI 19.03+/- 2.13 16.56 +/- 2.00 13.45+/- 1.50 16.49 +/- 3.83 SFDR07 Visitor's Center 13.66 +/- 0.75 15.13 +/- 1.62 13.03+/- 1.14 13.26 +/- 1.18

'TLD missing 66 I I I I II I I I ( I 1

I I f I I I I I I Januluy 1 -Lveumb&ri, 20U5 Docket Nos. 50-317/50-318/72-8 Table B Continued Direct Radiation (Results in Units of mR/90 days 4 2a)

SFDR08 NNW of ISFSI 40.54 +/- 3.85 40.33 +/- 4.50 31.99 +/- 1.28 29.84 +/- 4.65 SFDR09 SSE of ISFSI 14.95 +/- 0.91 15.33 +/- 1.14 13.77 +/- 1.31 15.53 +/- 2.19 SFDR10 NW of ISFSI 51.80 +/- 6.15 48.37 +/- 8.01 49.75 +/- 7.87 38.08 +/- 5.71 SFDR11 WNW ISFSI 33.38 +/- 8.29 37.08 11.19 27.88 +/- 5.86 33.29 +/- 6.09 SFDR12 WSW of ISFSI 41.22 +/- 7.89 36.21 + 3.18 33.41 +/- 8.17 42.05 +/- 5.93 SFDR13 South of ISFSI 22.21 +/- 0.80 23.26 i 2.08 20.35 +/- 2.49 20.04 +/- 3.37 SFDR14 SE of ISFSI 15.55 +/- 1.59 15.82 0.33 14.75 +/- 1.61 16.91 +/- 1.70 SFDR15 ENE of ISFSI 18.74 +/- 2.38 18.29 + 2.28 16.24 +/- 1.87 18.09 +/- 2.45 SFDR16 SSW of ISFSI 35.71 +/- 3.07 40.25 +/- 5.79 33.11 +/- 5.33 35.63 +/- 6.40 SFDRI7 NNE of ISFSI See text See text See text 36.04+/- 7.15 SFDR18 West of ISFSI See text See text See text 45.27 +/- 4.87 67

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK) 68

January I - December 31, 2003 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 of the 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-1 agree with the intercomparison laboratory results with the exception of a beta and a Ce-141 result for the filter sample type on 6/12/03 from Analytics. The filter sample was inadvertently inverted in the beta determination during the original analysis. This sample was correctly positioned in the counting chamber and rerun with the result of 68+1 pCi/filter, which is included in the table. This result was reevaluated using the NRC Resolution Test Criteria' and found to be in agreement. The Ce-141 result was also reevaluated using the same criteria and also found to be in agreement. The uncertainties for the Constellation Energy Laboratory's results and Analytics' results are +2U while the ERA laboratory's uncertainty is based on USEPA guidelines 2 . The results in this table are used as a check of instrumentation function and not meant to be used for reporting purposes of actual activity present in samples.

All the results contained in Table C-2 generally agree with their respective Constellation Energy Laboratory replicates and/or split laboratory samples, except for a Cs-1 37 result for a split soil sample collected 6/16/03 from SFS2 and the TLD replicate results for 9/30/03. The Cs-137 disagreement was due to the non-homogenous nature of the soil splits. When the split was returned to the Constellation Energy lab for analysis, the laboratory result was determined to be 131 +33 pCi/kg, which is in agreement with reported split result of 146 +4 pCi/kg. The disagreement on the TLD replicates was due to moisture present on some of the TLD assemblies which affected the instrument readings. The TLDs had been collected just after Hurricane Isabelle passed through the State of Maryland. As indicated in Table C-2 there were some instances where activity was observed in split samples, but not observed in the original sample.

This is due to the lower MDA achieved by the split laboratory using very long count times. Other samples whose nature generally precludes sample splitting are marked "**" in the Split Analysis 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, 2003 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK) 70

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 TABLE OF CONTENTS Quality Assurance Program Table Title Page C-1 Results of Participation in Cross Check Programs 73 C-2 Results of Quality Assurance Program 74 C-3 Teledyne Brown Engineering's Typical MDAs for Gamma Spectrometry 83 71

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK) 72

January I - December 31, 2003 Docket Nos. 50-317/50-318/72-8 TABLE C-1 Results of Participation in Cross Check Programs Sample Sample Type Isotope CGG Cross Check Date and Units Observed Laboratory's Lab Results' Results' 2/17/03 Water-pCi/L Ba-133 18+/-7 19+/-5 Co-60 41+/-6 37+/-5 Cs-1 34 14+/-4 18+/-5 Cs-1 37 45+/-8 44+/-5 Zn-65 60+/-17 60+/-6 5/19/03 Water-pCi/L H-3 1220+/-50 1250+/-331 Water-pCi/L 1-131 21+/-6 21+/-3 6/12/03 Filter-pCi/filter Beta 37+/-1 77+/-3 Corr. 68+/-1 6/12/03 Filter-pCi/filter Ce-141 203+/-9 172+/-6 Cr-51 181+/-62 145+/-5 Cs-134 57+/-3 63+/-2 Cs-137 148+/-6 140+/-5 Mn-54 128+/-6 113+/-4 Fe-59 77+/-9 60+/-2 Zn-65 128+/-10 110+/-4 Co-58 60+/-6 56+/-2 Co-60 88+/-4 80+/-3 8/18/03 Water-pCi/L Ba-133 17+/-3 21+/-5 Cs-1 34 30+/-3 33+/-5 Cs-1 37 47+/-5 44+/-5 Zn-65 60+/-10 60+/-6 Co-60 36+/-4 37+/-5 11/18/03 Water-pCi/L H-3 14400+/-109 14300+/-1430 Water-pCi/L 1-131 25+/-10 28+/-3

' See discussion at the beginning of this Appendix 73

January 1 - December 31, 2003 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 3

10-2 pCi/M Air Iodine-Al 1/06/03 1-131 <1.1 <1.2 **

Air lodine-A2 1/06/03 1-131 <1.9 <2.1 **

Air Filter -Al 1/06/03 Beta 1.1+/-0.2 1.2+/-0.2 **

Air Filter -A2 1/06/03 Beta 0.9+/-0.2 1.0+/-0.2 **

Air Filter -A3 1/06/03 Beta 0.8+/-0.2 0.8+/-0.2 **

Air Filter -A4 1/06/03 Beta 1.3+/-0.2 1.4+/-0.2 **

Air Filter -A5 1/06/03 Beta 1.0+/-0.2 1.1+/-0.2 **

Air Filter -SFAl 1/06/03 Beta 1.5+/-0.2 1.6+/-0.2 **

Air Filter -SFA2 1/06/03 Beta 1.2+/-0.2 1.4+/-0.2 **

Air Filter -SFA3 1/06/03 Beta 1.3+/-0.2 1.4+/-0.2 **

Air Filter -SFA4 1/06/03 Beta 1.2+/-0.2 1.3+/-0.2 **

10-2 pCi/M 3 Air Filter-Al 2/3/03 Beta 1.4+/-0.2 1.5+/-0.2 **

Air Filter-A2 2/3/03 Beta 1.0+/-0.2 1.0+/-0.2 **

Air Filter-A3 2/3/03 Beta 1.1+/-0.2 1.1+/-0.2 **

Air Filter-A4 2/3/03 Beta 2.0+/-0.2 2.1+/-0.2 **

Air Filter-A5 2/3/03 Beta 1.2+/-0.2 1.2+/-0.2 **

Air Filter-SFAI 2/3/03 Beta 2.2+/-0.2 2.4+/-0.2 **

Air Filter-SFA2 2/3/03 Beta 1.9+/-0.2 2.1+/-0.2 **

Air Filter-SFA3 2/3/03 Beta 1.6+/-0.2 1.6+/-0.2 **

Air Filter-SFA4 2/3/03 Beta 1.4+/-0.2 1.4+/-0.2 **

Air lodine-A3 2/3/03 1-131 <1.9 <2.2 Air lodine-A4 2/3/03 1-131 <1.5 <1.6 **

- The nature of these samples precluded splitting them with an independent laboratory.

(1) Result is below laboratory's LLD for this isotope 74

January 1 - December 31, 2003 Docket Nos. 50-317150-318/72-8 TABLE C Continued Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split And Location Date Analysis Analysis Analysis Analysis pCi/L Bay Water-Wa2 2/15/03 Tritium 767+44 794+44 784+/-139

- Bay Water-Wa2 2/28/03 Gamma <MDA <MDA <MDA 10.2 pCi/M3 Air Filter-Al 3/3/03 Beta 1.4+/-0.2 1.4+/-0.2 Air Filter-A2 3/3/03 Beta 1.0+/-0.2 1.0+/-0.2 Air Filter-A3 3/3/03 Beta 1.4+/-0.2 1.4+/-0.2 Air Filter-A4 3/3/03 Beta 2.0+/-0.2 2.2+/-0.2 Air Filter-A5 3/3/03 Beta 1.1+/-0.2 1.3+/-0.2 Air Filter-SFA1 3/3/03 Beta 2.0+/-0.2 2.0+/-0.2 Air Filter-SFA2 3/3/03 Beta 2.0+/-0.2 2.1+/-0.2 Air Filter-SFA3 3/3/03 Beta 1.4+/-0.2 1.5+/-0.2 Air Filter-SFA4 3/3/03 Beta 1.6+/-0.2 1.5+/-0.2 Air Iodine-Al 3/3/03 1-131 <1.1 <2.1 Air lodine-A2 3/3/03 1-131 <1.6 <2.7 pCi/Kg Oysters-la3 3/20/03 Ag-110m <MDA <MDA <MDA pCi/Kg

- Soil-SFS2 3/24/03 Cs-137 114+/-30 172+/-36 161+/-14 Soil-SFS3 3/24/03 Cs-137 416+/-49 396+/-47 369+/-15

- Vegetation-SFb1 3/24/03 Cs-137 <MDA <MDA <MDA Vegetation-SFb5 3/24/03 Cs-I 37 50+/-19 53+/-20 90+/-20 102 pCi/m 3 Air lodine-A3 4/07/03 1-131 <2.0 <1.7

- Air lodine-A4 4/07/03 1-131 <1.2 <1.3 **

-**The nature of these samples precluded splitting them with an independent laboratory.

75

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 TABLE C 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 Filter-Al 4/07/03 Beta 1.2+/-0.2 1.3+/-0.2 **

Air Filter-A2 4/07/03 Beta 1.1+/-0.2 1.1+/-0.2 **

Air Filter-A3 4/07/03 Beta 1.2+/-0.2 1.4+/-0.2 Air Filter-A4 4/07/03 Beta 1.6+/-0.2 1.7+/-0.2 Air Filter-A5 4/07/03 Beta 1.4+/-0.2 1.5+/-0.2 **

Air Filter-SFAl 4/07/03 Beta 1.3+/-0.2 1.4+/-0.2 Air Filter-SFA2 4/07/03 Beta 1.2+/-0.2 1.4+/-0.2 **

Air Filter-SFA3 4/07/03 Beta 1.7+/-0.2 1.7+/-0.2 Air Filter-SFA4 4/07/03 Beta 1.1+/-0.2 1.1+/-0.2 pCi /L Bay Water-Wa2 4/30/03 Gamma <MDA <MDA <MDA 102 pCi/m 3 Air Iodine-Al 5/5/03 1-131 <1.2 <1.3 Air Iodine-A2 5/5/03 1-131 <2.2 <2.1 **

Air Filter-Al 5/5/03 Beta 1.2+/-0.2 1.2+/-0.2 **

Air Filter-A2 5/5/03 Beta 0.9+/-0.2 1.0+/-0.2 **

Air Filter-A3 5/5/03 Beta 1.3+/-0.2 1.3+/-0.2 **

Air Filter-A4 5/5/03 Beta 1.8+/-0.2 1.9+/-0.2 **

Air Filter-A5 5/5/03 Beta 1.2+/-0.2 1.3+/-0.2 **

Air Filter-SFA1 5/5/03 Beta 2.3+/-0.3 2.3+/-0.3 Air Filter-SFA2 5/5/03 Beta 1.4+/-0.2 1.5+/-0.2 **

Air Filter-SFA3 5/5/03 Beta 1.7+/-0.2 1.6+/-0.2 **

Air Filter-SFA4 5/5/03 Beta 1.1+/-0.2 1.1+/-0.2 **

- The nature of these samples precluded splitting them with an independent laboratory.

76

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 TABLE C Continued Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split And Location Date Analysis Analysis Analysis Analysis 3

102 pCi/M Air Filter-Al 6/3/03 Beta 0.9+/-0.1 1.0+/-0.1 **

Air Filter-A2 6/3/03 Beta 0.9+/-0.2 0.9+/-0.2 **

Air Filter-A3 6/3/03 Beta 0.8+/-0.2 0.9+/-0.2 **

Air Filter-A4 6/3/03 Beta 1.1+/-0.2 1.0+/-0.2 Air Filter-A5 6/3/03 Beta 0.9+/-0.2 1.1+/-0.2 **

Air Filter-SFAl 6/3/03 Beta 1.0+/-0.2 1.0+/-0.2 **

Air Filter-SFA2 6/3/03 Beta 1.1+/-0.2 1.1+/-0.2 **

Air Filter-SFA3 6/3/03 Beta 1.1+/-0.2 1.2+/-0.2 Air Filter-SFA4 6/3/03 Beta 0.7+/-0.2 0.5+/-0.2 **

Air Iodine-Al 6/3/03 1-131 <1.1 <1.1 **

Air lodine-A2 6/3/03 1-131 <1.6 <1.9 pCi/Kg

_ Shoreline-Wb1 6/5/03 Gamma <MDA <MDA <MDA 3

103 pCi/m Air Filters-Al 6/15/03 Gamma <MDA <MDA <MDA Air Filters-A2 6/15/03 Gamma <MDA <MDA <MDA Air Filters-A3 6/15/03 Gamma <MDA <MDA <MDA Air Filters-A4 6/15/03 Gamma <MDA <MDA <MDA Air Filters-A5 6/15/03 Gamma <MDA <MDA <MDA Air Filters-SFAl 6/15/03 Gamma <MDA <MDA <MDA Air Filters-SFA2 6/15/03 Gamma <MDA <MDA <MDA Air Filters-SFA3 6/15/03 Gamma <MDA <MDA <MDA Air Filters-SFA4 6/15/03 Gamma <MDA <MDA <MDA

- The nature of these samples precluded splitting them with an independent laboratory.

77

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 TABLE C Continued Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split And Location Date Analysis Analysis Analysis Analysis pCi/kg Soil-SFS2 6/16/03 Cs-i 37 86+/-40 98+/-28 146+/-4(1)

Soil-SFS3 6/16/03 Cs-137 396+/-66 276+/-48 461+/-12 Vegetation-SFb2 6/16/03 Gamma <MDA <MDA <MDA Vegetation-SFb3 6/16/03 Gamma <MDA <MDA <MDA mRf90 Days DR05 6/30/03 TLD 12.71+/-1.03 12.34+/-0.76 **

DR06 6/30/03 TLD 10.84+/-0.66 10.86+/-0.95 **

DR07 6/30/03 TLD 11.06+/-0.79 11.03+/-1.15 DR08 6/30/03 TLD 15.42+/-0.89 16.10+/-0.87 **

DR09 6/30/03 TLD 12.13+/-1.04 12.44+/-0.61 **

DR10 6/30/03 TLD 11.30+/-0.53 11.48+/-1.32 DR11 6/30/03 TLD 11.69+/-0.98 11.89+/-1.14 DR29 6/30/03 TLD 15.71+/-0.97 15.85+/-1.28 **

DR31 6/30/03 TLD 16.96+/-0.79 16.70+/-1.53 **

SFDR14 6/30/03 TLD 16.05+/-1.16 16.45+/-0.31 **

SFDR15 6/30/03 TLD 18.29+/-2.28 18.48+/-0.96 10-2 pCi/im3 Air Filter-Al 7/07/03 Beta 1.0+/-0.2 1.2+/-0.2 **

Air Filter-A2 7/07/03 Beta 0.5+/-0.2 0.4+/-0.2 **

Air Filter-A3 7/07/03 Beta 0.8+/-0.2 1.0+/-0.2 **

Air Filter-A4 7/07/03 Beta 2.2+/-0.2 2.2+/-0.2 **

Air Filter-A5 7/07/03 Beta 1.3+/-0.2 1.5+/-0.2 **

Air Filter-SFA1 7/07/03 Beta 1.7+/-0.2 1.9+/-0.2 **

Air Filter-SFA2 7/07/03 Beta 1.6+/-0.2 1.6+/-0.2 Air Filter-SFA3 7/07/03 Beta 1.5+/-0.2 1.6+/-0.2 **

Air Filter-SFA4 7/07/03 Beta 0.6+/-0.2 0.6+/-0.2 **

Air lodine-A3 7/07/03 1-131 <1.5 <1.8 **

Air lodine-A4 7/07/03 1-131 <1.7 <1.7 **

- The nature of these samples precluded splitting them with an independent laboratory.

(1) See discussion at the beginning of this Appendix 78

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 TABLE C Continued Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split And Location Date Analysis Analysis Analysis Analysis pCi/L Bay Water-Wa2 8/4/03 Gamma <MDA <MDA <MDA 10-2 pCi/M3

- Air Filter-Al 8/4/03 Beta 1.0+/-0.2 1.0+/-0.2 **

Air Filter-A2 8/4/03 Beta 0.6+/-0.2 0.4+/-0.2 Air Filter-A3 8/4/03 Beta 0.8+/-0.2 0.8+/-0.2 **

Air Filter-A4 8/4/03 Beta 1.4+/-0.2 1.2+/-0.2 **

Air Filter-A5 8/4/03 Beta 0.9+/-0.2 1.0+/-0.2 **

Air Filter-SFA1 8/4/03 Beta 0.8+/-0.2 0.8+/-0.2 **

- Air Filter-SFA2 8/4/03 Beta 1.0+/-0.2 1.0+/-0.2 **

Air Filter-SFA3 8/4/03 Beta 1.0+/-0.2 1.0+/-0.2 **

Air Filter-SFA4 8/4/03 Beta 0.7+/-0.2 0.7+/-0.2 Air Iodine-Al 8/4/03 1-131 <1.3 <1.7 **

Air Iodine-A2 8/4/03 1-131 <1.6 <1.7 **

pCi/L Bay Water-Wa2 8/15/03 Tritium 207+/-41 162+/-41 276+/-123 pCi /kg Vegetation-lb4 8/25/03 Gamma <MDA <MDA <MDA Vegetation-lb5 8/25/03 Gamma <MDA <MDA <MDA Vegetation-lb6 8125/03 Gamma <MDA <MDA <MDA Vegetation-lb7 8/25/03 Gamma <MDA <MDA <MDA Vegetation-lb8 8/25/03 Gamma <MDA <MDA <MDA Vegetation-lb9 8/25/03 Gamma <MDA <MDA <MDA pCikg Fish-lal 7/28/03 Gamma <MDA <MDA <MDA Oysters-la3 8/14/03 Ag-I 1Om <MDA <MDA <MDA

-**The nature of these samples precluded splitting them with an independent laboratory.

79

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 TABLE C 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 lodine-A3 9/8/03 1-131 <1.7 <11.9 Air lodine-A4 9/8/03 1-131 <1.6 <1.7 **

Air Filter-Al 9/8/03 Beta (1) (1)

Air Filter-A2 9/8/03 Beta 0.6+/-0.2 0.7+/-0.2 **

Air Filter-A3 9/8/03 Beta 1.3+/-0.2 1.3+/-0.2 **

Air Filter-A4 9/8/03 Beta 1.5+/-0.2 1.5+/-0.2 Air Filter-A5 9/8/03 Beta 1.6+/-0.2 1.7+/-0.2 **

Air Filter-SFA1 9/8/03 Beta 1.6+/-0.2 1.6+/-0.2 **

Air Filter-SFA2 9/8/03 Beta 1.3+/-0.2 1.3+/-0.2 Air Filter-SFA3 9/8/03 Beta 1.2+/-0.2 1.3+/-0.2 Air Filter-SFA4 9/8/03 Beta 1.3+/-0.2 1.3+/-0.2 mR/90 Days DR05 9/30/03 TLD(1) 11.62+/-0.75 11.30+/-0.72 **

DR06 9/30/03 TLD 9.88+/-1.43 7.45+/-1.94 **

DR07 9/30/03 TLD 9.65+/-1.03 8.40+/-0.66 **

DR08 9/30/03 TLD 14.39+/-0.23 12.28+/-1.29 DR09 9/30/03 TLD 11.11+/-0.75 9.35+/-0.75 DRI 0 9/30/03 TLD 10.34+/-0.64 8.79+/-0.99 DR11 9/30/03 TLD 10.84+/-1.02 7.61+/-3.32 DR29 9/30/03 TLD 13.00+/-1.06 9.93+/-1.14 **

DR31 9/30/03 TLD 15.33+/-3.54 10.05+/-1.07 **

SFDR14 9/30/03 TLD 14.75+/-1.61 9.48+/-0.80 SFDR15 9/30/03 TLD 16.24+/-1.87 11.06+/-1.19 **

10-2 pCi/m3 Air lodine-A3 10/6/03 1-131 <1.2 <1.4 **

Air lodine-A4 10/6/03 1-131 <2.1 <2.2

- The nature of these samples precluded splitting them with an independent laboratory.

(1) See discussion at the beginning of this Appendix 80

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 TABLE C 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 Filter-Al 10/13/03 Beta 3.0+/-0.2 3.2+/-0.2 **

Air Filter-A2 10/13/03 Beta 2.8+/-0.2 2.9+/-0.2 Air Filter-A3 10/13/03 Beta 2.1+/-0.2 2.0+/-0.2 **

Air Filter-A4 10113/03 Beta 3.0+/-0.2 3.1+/-0.2 **

Air Filter-A5 10/13/03 Beta 2.0+/-0.2 3.2+/-0.2 Air Filter-SFAl 10/13/03 Beta 3.4+/-0.2 3.4+/-0.2

- Air Filter-SFA2 10/13/03 Beta 2.8+/-0.2 2.8+/-0.2 Air Filter-SFA3 10/13/03 Beta 2.2+/-0.2 2.4+/-0.2 Air Filter-SFA4 10/13/03 Beta 1.9+/-0.2 2.0+/-0.2 pCi /kg Vegetation-lbl 11/3/03 Gamma <MDA <MDA <MDA Vegetation-lb3 11/3/03 Cs-137 <MDA <MDA Cs-137=1.4(1)

_ Vegetation-lb4 11/3/03 Cs-137 <MDA <MDA Cs-137=1.5(1)

Vegetation-lb6 11/3/03 Gamma <MDA <MDA <MDA Vegetation-lb7 11/3/03 Co-60 <MDA <MDA Co-60=1.9(1)

Vegetation-lb9 11/3/03 Gamma <MDA <MDA <MDA 102 pCi/m 3 Air Filter-Al 11/03/03 Beta 2.0+/-0.2 2.3+/-0.2 Air Filter-A2 11103/03 Beta 2.1+/-0 .2 2.2+/-0.2 **

Air Filter-A3 11/03/03 Beta 1.7+/-0.2 1.8+/-0.2 Air Filter-A4 11/03/03 Beta 2.2+/-0.2 2.2+/-0.2 Air Filter-A5 11/03/03 Beta 1.6+/-0.2 1.6+/-0.2

_ Air Filter-SFA1 11/03/03 Beta 2.1+/-0.2 2.3+/-0.2 Air Filter-SFA2 11/03/03 Beta 2.1+/-0.2 2.1+/-0.2 Air Filter-SFA3 11103/03 Beta 2.1+/-0.2 2.3+/-0.2

-Air Filter-SFA4 11/03/03 Beta 1.9+/-0.2 2.0+/-0.2 Air Iodine-Al 11/03/03 1-131 <1.2 <1.2

- Air lodine-A2 11/03/03 1-131 <1.7 <1.6

-**The nature of these samples precluded splitting them with an independent laboratory.

(1) Result is below the Constellation Energy Laboratory's LLD for this isotope.

81

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 TABLE C Continued Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split And Location Date Analysis Analysis Analysis Analysis pCiIL Bay Water-Wa2 12/05/02 Gamma <MDA <MDA Co-60=0.6(1) 3 10.2 pCin Air Filter-Al 12/08/03 Beta 1.2+/-0.2 1.4+/-0.2 Air Filter-A2 12/08/03 Beta 1.3+/-0.3 1.5+/-0.2 Air Filter-A3 12/08/03 Beta 1.1+/-0.2 1.1+/-0.2 Air Filter-A4 12/08/03 Beta 1.5+/-0.2 1.5+/-0.2 **

Air Filter-A5 12/08/03 Beta 1.2+/-0.2 1.4+/-0.3 Air Filter-SFAI 12/08/03 Beta 1.2+/-0.2 1.3+/-0.2 Air Filter-SFA2 12/08/03 Beta 1.2+/-0.2 1.5+/-0.2 Air Filter-SFA3 12/08/03 Beta 1.2+/-0.2 1.3+/-0.2 Air Filter-SFA4 12/08/03 Beta 1.2+/-0.2 1.2+/-0.2 Air Iodine-Al 12/08/03 1-131 <1.5 <1.5 Air lodine-A2 12/08/03 1-131 <1.5 <1.7 3

10 pC/r Air Filters-Al 12/15/03 Gamma <MDA <MDA <MDA Air Filters-A2 12/15/03 Gamma <MDA <MDA <MDA Air Filters-A3 12/15/03 Gamma <MDA <MDA <MDA Air Filters-A4 12/15/03 Gamma <MDA <MDA <MDA Air Filters-A5 12/15/03 Gamma <MDA <MDA <MDA Air Filters-SFAI 12/15/03 Gamma <MDA <MDA <MDA Air Filters-SFA2 12/15/03 Gamma <MDA <MDA <MDA Air Filters-SFA3 12/15/03 Gamma <MDA <MDA <MDA Air Filters-SFA4 12/15/03 Gamma <MDA <MDA <MDA

- The nature of these samples precluded splitting them with an independent laboratory (1) Result is below the Constellation Energy Laboratory's LLD for this isotope.

82

January I - December 31, 2003 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/l 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 83

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK) 84

January 1 - December 31, 2003 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.

Discussion Table D-1 Land Use Survey A Land Use Survey was conducted to identify, Distance From Plant within a distance of 5 miles, the location of the (miles) nearest milk animal, the nearest residence, and Sector Residence Garden the nearest garden greater than 50 m2 in each of the nine sectors over land. A detailed description SE 1.4 1.4 SSE 1.7 1.8 of the Land Use Survey is given in a separate document (Ref. 5). The position of the nearest S 1.6 2.0 residence and garden in each sector out to 5 miles SSW 1.6 1.6 SW 1.2 1.3 is given in the adjacent table. No dairy animal was found within 5 miles in any direction. There WSW 1.0 1.3 are new residences located in the WNW sector W 1.3 1.4 within the 5-mile radius, but does not challenge WNW 1.5 1.5 the location of the nearest residence or garden. NW 2.0 2.0 The closest. residence is situated in the WSW sector and the nearest garden is in the WSW sector, which are in the least prevalent wind directions. In the S, SSE, and SE sectors, 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 of 0.4 miles, and another is situated near the site boundary in the SSE sector at a distance of 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's meteorological data was performed, and no significant impact from the plant was found.

85

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK) 86

January 1 - December 31, 2003 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. 2). 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-9 shows the average monthly direct radiation as measured by the pressurized ion chamber at five locations. The dose rate at the Met Station, PIC3, during the month of August was high. This result was due to spurious data spikes affecting the dose rate. These spurious spikes were caused by a corroded signal cable, which was subsequently cleaned and refurbished. The PIC was then put back in operation.

Table E- 1I 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.

87

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 (LEFT BLANK) 88

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 TABLE OF CONTENTS Additional Samples and Analysis Results Table Title Page E-1 Locations of Non-ODCM Environmental Sampling Stations for Calvert Cliffs Nuclear Power Plant .90 E-2 Synopsis of 2003 Calvert Cliffs Nuclear Power Plant Non-ODCM Radiological Environmental Monitoring Program .91 E-3 Annual Summary for Calvert Cliffs Nuclear Power Plant Units 1 & 2 Non-ODCM Radiological Environmental Monitoring Program .92 E-4 Concentration of Gamma Emitters in Bottom Sediment .93 E-5 Concentration of Iodine-1 31 in Filtered Air .94 E-6 Concentration of Beta Emitters in Air Particulates .96 E-7 Concentration of Gamma Emitters in Air Particulates .98 E-8 Concentration of Tritium and Gamma Emitters in Taylors Island Well Water .99 E-9 Direct Radiation as Measured in Pressurized Ion Chamber .100 E-10 Direct Radiation .................................. 101 E-1 1 Direct Radiation from Resin Storage Area .................................. 102 89

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 TABLE E-1 Locations of Non-ODCM 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 OSGDRI 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 PICI 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 RPDR10 Resin Storage Area - South Fence Lower 0.7 0.4 SW RPDRI 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 Intake Area 0.2 0.1 NE Wbs2 Discharge Area 0.3 0.2 N Wbs3 Long Beach 4.4 2.7 NW 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.

90

r r r I I I? [ I r XI I , anuLy -ditalbel i,200!

Docket Nos. 50-317/50-318/72-8 Table E-2 Synopsis of 2003 Calvert Cliffs Nuclear Power Plant Non-ODCM Radiological Environmental Monitoring Program Sample Type Sampling Number of Locations Number Collected Analysis Analysis Frequency1 Number Analyzed Freauencvl Aquatic Environment Bottom Sediment Q 4 16 Gamma 0 16 Atmospheric Environment Air Iodine2 W 7 357 1-131 W 357 Air Particulates4 W 3 151 Gross Beta W 151 Gamma MC 36 Direct Radiation Pressurized Ion M 6 72 Gamma M 72 Chamber Ambient Radiation Q 20 474 -TLD Q 4 474 Terrestrial Environment Ground water M 1 12 Gamma M 12 H-3 M 12

'W-Weekly, M-monthly, Q-quarterly, SA-semiannual, A-annual, C-composite 2 The collection device contains silver zeolite 3Beta counting is performed after >= 72 hour8.333333e-4 days 0.02 hours 1.190476e-4 weeks 2.7396e-5 months decay. Gamma spectroscopy performed on monthly composites of weekly samples 91

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 Table E-3 Annual Summary for Calvert Cliffs Nuclear Power Plant Units 1 & 2 Non-ODCM Radiological Environmental Monitoring Program Medium or Pathway Type and Total Lower Limit of Indicator Locations Location with Highest Annual Control Locations Sampled (Unit of Number of Analyses Detection (LLD) Mean (F)lRangel Highest Annual Mean (F) / Range' Mean (F)l/Rangel Measurement) Performed Mean Name/Distance 2 rlirnrtnn Aquatic Environment Bottom Gamma (16) 17 152 (9/12) Long Beach Wbs3 174 (4/4) 144 (4/4)

Sediment Cs-1 37 (25-206) 4.4 km NW (136-206) (123-168)

(pCi/kg)

Atmospheric Environment Air Particulates Gross Beta (151) 0.5 1.3 (100/100) Cambridge CAM 1.6 (48/52) 1.5 (51/51)

(10-2pC/r 3 ) (0.4-3.3) 32 km NE (0.7-3.3) (0.7-3.5)

Direct Radiation Ambient TLD (474) -- 16.37 (474/474) West Fence Right 23.70 (24/24) 13.39(72/72)

Radiation (8.98-31.33) RPDR07 0.8 km (18.63-31.33) 9.95-17.15 (mR/90 days)

Pressurized1 Inn Inni7ztinn Chamhbr - A 925 (n/6An NNW nf IAFSI PI(CA 11 33 £1 9/192 7R I Ol1A1 Chamber (72) 0,**

6..e km .SW (3.71-12.62) 0.6 km SW (11.46-12.62) (5.14-6.34)

(mR/30 days)

' Mean and range based upon detectable measurements only. Fraction (F) of detectable measurements at specified location is indicated in parentheses From the centerpoint between the two containment buildings 92 l I I I I I I I II I I i

January I - December 31, 2003 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 Wbs1 3/20/2003 25 +/- 17 v

Intake Area 6/24/2003 8/14/2003 I

10/21/2003 Wbs2 3/20/2003 165 +/- 49

Discharge Area 6/24/2003 155 +/- 38

8/14/2003 139 +/- 36

10/21/2003 185 +/- 41

Wbs3 3/20/2003 206 +/- 50

Long Beach 6/24/2003 183 +/- 48

8/14/2003 136 +/- 50

10/21/2003 171 +/-56

Wbs4 2 3/20/2003 168 +/- 45

Camp Conoyi Rocky Point 6/24/2003 127 +/- 41

8/14/2003 158 +/- 39

10/21/2003 123 +/- 31 *

' This Isotope <MDA 2

Control Location

~* All Other Non-Natural Gamma Emitters <MDA 93

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 Table E-5 Concentration of Iodine-131 in Filtered Air (Results in units of 10 pCi/m3 + 2cr)

Start Date Stop Date A6 A7 CAM SFAI SFA2' SFA3 SFA4 Long Taylors Cambridge MET Visitors NNW of SSE of Beach Island Station Center ISFSI ISFSI 12/30/2002 1/6/2003 *

2 * * *

1/6/2003 1/13/2003 * * * * * *

1/13/2003 1/20/2003 * * * * * *

1/20/2003 1/27/2003 * * * * * *

1/27/2003 2/3/2003 * * * * * *

213/2003 2110/2003 * * * * * *

2/10/2003 2119/2003 * * * * * *

2119/2003 2/24/2003 * * * * * *

2/24/2003 3/3/2003 * * * * * *

3/3/2003 3/10/2003 * * * * * *

3/10/2003 3/17/2003 * * * * *

3/17/2003 3/24/2003 * * * * * *

3/24/2003 3/31/2003 * * * * * *

3/31/2003 4/7/2003 * * * * * *

4/7/2003 4/14/2003 * * * * * *

4/14/2003 4/21/2003 * * * * * *

4/21/2003 4/28/2003 * * * * * *

4/28/2003 5/5/2003 * * * * * *

5/5/2003 5/12/2003 * * * * * *

5/12/2003 5/19/2003 * * * * *

5/19/2003 5/26/2003 * * * * * *

5/26/2003 6/212003 * * * * * *

6/2/2003 6/9/2003 * * * * * *

6/9/2003 6/16/2003 * * * * * *

6/16/2003 6/23/2003 * * * * * *

6/23/2003 6/30/2003 * * * * * *

6/30/2003 7/7/2003 *

2 * * *

7/7/2003 7/14/2003 * * * * * *

7/14/2003 7/21/2003 * * * * * *

7/21/2003 7/28/2003 * * * * * *

7/28/2003 8/4/2003 * * * * * *

8/4/2003 8/11/2003 * * * * * *

8/11/2003 8/18/2003 * * * * *

8/18/2003 8/25/2003 *

2 * * *

8/25/2003 9/1/2003 * * * * * * *

' Control Location 2 Sampler malfimction/loss of power

<MDA 94

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 Table E Continued Concentration of Iodine-131 in Filtered Air (Results in units of 10-3 pCi/M3 +/- 2a) 6- Start Date Stop Date A6 A7 CAM SFA1 SFA2' SFA3 SFA4 Long Taylors Cambridge MET Visitors NNW of SSE of Beach Island Station Center ISFSI ISFSI 9/1/2003 9/8/2003 * * * * * *

9/8/2003 9/15/2003 * * * * * *

n14 ^szifnnQ

,,I I UJl Uv.jS ;I -

JEffnnl o u 9/22/2003 9/29/2003 * * * * * *

9129/2003 1016/2003 * * * * *

_ 10/6/2003 10113/2003 * * * * * *

10/1312003 10/20/2003 * * * * * *

10/20/2003 10/27/2003 * * * * * *

10/27/2003 11/3/2003 * * * * * *

11/3/2003 11/10/2003 * * * * * *

11/10/2003 11/17/2003 * * * * * *

11/17/2003 11/24/2003 * *

2 * *

11/24/2003 12/1/2003 *

12/1/2003 12/8/2003 * * * * * *

12/8/2003 12/15/2003 * * * * * *

12/15/2003 12/22/2003 * * * * *

12/22/2003 12/29i2003

' Control Location h2 Sampler malfunction/loss of power

<MDA 95

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 Table E-6 Concentration of Beta Emitters in Air Particulates (Results in units of 1O2 pCi/rn3 X 2cr)

Start Date Stop Date A6 A7I CAM Long Beach Taylors Island Cambridge 2

12/30/2002 1/612003 0.8 +/- 0.2 1.1 +/-0.2 1/6/2003 1/13/2003 1.2 +/- 0.2 1.9 +/- 0.2 2.0+/-0.2 1/13/2003 1/20/2003 1.3 +/- 0.2 2.2 +/- 0.2 2.2 +/- 0.2 1/20/2003 1/27/2003 1.3 +/- 0.2 1.8 +/- 0.2 2.0 +/- 0.2 1/2712003 2/3/2003 1.0 +/- 0.2 1.4 +/- 0.2 1.4 +/- 0.2 2/3/2003 2/10/2003 1.2 +/- 0.2 2.0 +/- 0.2 2.0 +/- 0.2 2/10/2003 2/19/2003 1.2 +/- 0.2 1.3 +/- 0.1 1.2 +/- 0.2 2/19/2003 2/24/2003 0.8 +/- 0.2 1.6 +/- 0.2 1.6 +/- 0.2 2/24/2003 3/3/2003 1.0 +/- 0.2 1.7 +/- 0.2 1.7 +/- 0.2 3/3/2003 3/10/2003 1.2 +/- 0.2 2.0 +/- 0.2 2.1 +/- 0.2 3/10/2003 3/17/2003 1.2 +/- 0.2 1.i+/- 0.2 1.6 +/- 0.2 3/17/2003 3/24/2003 1.0 +/- 0.2 1.4 i0.2 1.3 +/- 0.2 3/24/2003 3/31/2003 1.0 +/- 0.2 1.5 0.2 1.3+/- 0.2 3/31/2003 4/7/2003 1.4 +/- 0.2 1.3 +/- 0.2 1.3 +/- 0.2 4/7/2003 4/14/2003 0.7 +/- 0.2 1.2 +/- 0.2 1.3 +/- 0.2 4/14/2003 4/21/2003 1.3 +/- 0.2 1.6 0.2 1.8 +/- 0.2 4/21/2003 4128/2003 0.9 +/- 0.2 1.1 i 0.2 1.4 +/- 0.2 4/28/2003 5/5/2003 1.0 +/- 0.2 1.4 +/- 0.2 1.4 +/- 0.2 5/5/2003 5/12/2003 0.5 +/- 0.1 1.0 +/- 0.2 1.0 +/- 0.2 5/12/2003 5/19/2003 0.5+/-0.2 1.1 +/-0.2 5/19/2003 5/2612003 0.7 +/- 0.1 0.9 +/- 0.2 1.0 +/- 0.2 5(26/2003 6/2/2003 0.5 +/- 0.1 1.0 +/- 0.2 1.4 +/- 0.2 6/2/2003 6/912003 0.6 +/- 0.2 0.9 +/- 0.3 1.0 +/- 0.3 6/9/2003 6/16/2003 0.6 +/- 0.2 1.3 +/- 0.2 1.6 +/- 0.3 6/16/2003 6/23/2003 0.4 +/- 0.2 1.0 +/- 0.2 1.2 +/- 0.2 6/23/2003 6/30/2003 0.8 +/- 0.2 1.4 +/- 0.2 3.3 +/- 0.5 6/30/2003 7/7/2003 1.4 +/- 0.2 1.2 +/- 0.2 2 7/7/2003 7/14/2003 0.6 +/- 0.2 1.5 +/- 0.2 1.5 +/- 0.2 7/14/2003 7/21/2003 0.6 +/- 0.2 1.1 +/- 0.2 2.0 +/- 0.3 7/21/2003 7/28/2003 0.7 +/- 0.2 0.9 +/- 0.2 1.3 +/- 0.3 7/28/2003 8/4/2003 0.5 +/- 0.2 0.9 +/- 0.2 1.5 +/- 0.3 8/4/2003 8/11/2003 0.6 +/- 0.2 0.7 +/- 0.2 1.1 +/- 0.3 8/11/2003 8/18/2003 0.7 +/- 0.2 1.0 +/- 0.2 2 8/18/2003 8/25/2003 0.9 +/- 0.2 2.0 +/- 0.2 2 8/25/2003 9/1/2003 0.8 +/- 0.2 1.8 +/- 0.3 1.8 +/- 0.2

' Control Location 2 Sampler malfimction/loss of power 96

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 Table E Continued Concentration of Beta Emitters in Air Particulates (Results in units of 10-2 pCi/m3 :E 2cr)

Start Date Stop Date A6 A71 CAM Lona Beach Tavlors Island Cambridae

_ 9/1/2003 9/8/2003 1.0 i 0.2 1.8 +/- 0.3 0.8 +/- 0.1 9/8/2003 9/15/2003 1.5+/- 0.2 1.1 +/-0.2 0.7 +/- 0.1 9/15/2003 9/22/2003 2.4 +/- 0.3 1.5 +/- 0.3 0.9 +/- 0.1 9/22/2003 9/29/2003 1.7 +/- 0.2 2.1 +/- 0.2 1.3 +/- 0.1 9/29/2003 10/6/2003 1.0 +/- 0.2 1.8 +/- 0.3 1.6 +/- 0.2 10/6/2003 10/13/2003 2.0 +/- 0.2 3.5 +/- 0.3 2.6 +/- 0.2 10/13/2003 10/20/2003 1.3 +/- 0.2 2.2 +/- 0.2 2.2 +/- 0.2 10/20/2003 10/27/2003 1.4+/-0.3 1.1 +/- 0.2 1.1 +/-0.2 10/27/2003 11/3/2003 2.0 +/- 0.3 2.4 +/- 0.2 2.3 +/- 0.2 11/3/2003 11/10/2003 1.3 +/- 0.3 1.6 +/- 0.2 1.4 +/- 0.2 11/10/2003 11/17/2003 2.3 +/- 0.3 2.0 +/- 0.2 1.8 i 0.2 11/17/2003 11/24/2003 2.1 +/- 0.3 1.5 +/- 0.2 1.7 +/- 0.2

-11/24/2003 12/1/2003 2.3 +/- 0.3 2.0 +/- 0.2 2.2 +/- 0.2 12/1/2003 12/8/2003 1.3 +/- 0.3 1.2 +/- 0.2 1.1 +/- 0.2 12/8/2003 12/15/2003 1.3 +/- 0.3 1.3 +/- 0.2 1.2 +/- 0.2 12/15/2003 12/22/2003 1.5 +/- 0.2 1.6 +/- 0.2 1.7 +/- 0.2 12/22i2003 12/29/2003 1.5 +/- 0.2 2.6 +/- 0.2 2.4 +/- 0.2

' Control Location 97

January I - December 31, 2003 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 A6 A7' CAM Date Long Beach Tavlors Island Cambridge 1/15/2003 * *

2/15/2003 * *

3/15/2003

4/15/2003

5/15/2003 * *

6/15/2003 * *

7/15/2003 * *

8/15/2003 * *

9/1512003 * *

10/15/2003 * *

11/15/2003 * *

12/15/2003 * * *

' Control Location

Non-Natural Ganmma Ernitters <MDA 98

January 1 - December 31, 2003 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/r 3 + 2a)

Sample H-3 Gamma Emitters Date 2/4/2003 <38

3/412003 <38

4/112003 <38

4/29/2003 <40

6/4/2003 <40

7/1/2003 <40

8/5/2003 <43

8/26/2003 <41

10/1/2003 <41

10/28/2003 <43

12/2/2003 <43

12/3112003 <43 *

Non-Natural Gamma Emitters <MDA 99

January 1 - December 31, 2003 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%)

SaMrle Code Month mR/30 Days Month mR/30 Days PIC1 I JAN 5.61 +/- 0.56 FEB 5.14 +/- 0.51 Taylor's Island MAR 5.54 +/- 0.55 APR 5.56 +/- 0.56 MAY 5.65 +/- 0.57 JUN 5.89 +/- 0.59 JUL 5.98 +/- 0.60 AUG 5.89 +/- 0.59 SEP 5.85 +/- 0.58 OCT 6.34 +/- 0.63 NOV 6.16 +/- 0.62 DEC 5.79 +/- 0.58 PIC2 JAN 4.01 +/- 0.40 FEB 3.85 +/- 0.38 Entrance to Camp MAR 3.95 +/- 0.40 APR 4.67 +/- 0.47 Conoy MAY 3.89 +/- 0.39 JUN 3.74 +/- 0.37 JUL 3.78 +/- 0.38 AUG 3.75 +/- 0.38 SEP 3.71-+/- 0.37 OCT 3.80 +/- 0.38 NOV 3.94 +/- 0.39 DEC 4.15 +/- 0.42 PIC3 JAN 5.01 +/- 0.50 FEB 4.79 +/- 0.48 MET Station MAR 4.87 +/- 0.49 APR 4.83 +/- 0.48 MAY 4.84 +/- 0.48 JUN 4.72 +/- 0.47 JUL 4.76 +/- 0.48 AUG 8.67 +/- 0.87 SEP 4.68 +/- 0.47 OCT 4.82 +/- 0.48 NOV 4.74 +/- 0.47 DEC 4.84 +/- 0.48 PIC4 JAN 12.06 +/- 1.21 FEB 11.84 +/- 1.18 NNW of ISFSI MAR 12.62 +/- 1.26 APR 12.26 +/- 1.23 MAY 11.73 +/- 1.17 JUN 11.92 +/- 1.19 JUL 11.73+/- 1.17 AUG 11.62 +/- 1.16 SEP 11.46 +/- 1.14 OCT 11.65+/- 1.16 NOV 11.49+/- 1.15 DEC 11.57 +/- 1.16 PIC5 JAN 5.77+/-0.58 FEB 5.43 +/- 0.54 SSE of ISFSI MAR 5.63 +/-0.56 APR 5.52 +/- 0.55 MAY 5.51 +/- 0.55 JUN 5.36 +/-0.54 JUL 5.35 +/- 0.54 AUG 5.30 +/- 0.53 SEP 5.35 +/- 0.54 OCT 5.78 +/- 0.58 NOV 5.85 +/- 0.58 DEC 6.03 +/- 0.60 PIC8 JAN 4.98 +/- 0.50 FEB 4.72 +/- 0.47 Visitor's Center MAR 4.78 +/- 0.48 APR 4.77 +/- 0.48 MAY 4.78 +/- 0.48 JUN 4.77 +/- 0.48 JUL 4.90 +/- 0.49 AUG 4.84 +/- 0.48 SEP 4.72 +/- 0.47 OCT 4.79 +/- 0.48 NOV 4.61 +/- 0.46 DEC 4.66 +/- 0.47

' Control Location 100

r r rI (r r I I t ( I I A -antL.)-I.nbefJI, 20d, Docket Nos. 50-317/50-318/72-8 Table E-10 Direct Radiation (Results in units of mR/90 days 4 2c)

Site Code Location First Quarter Second Quarter Third Quarter Fourth Quarter DR24 Rt. 4 and Parran Rd. 12.76 +/- 1.19 12.48 +/- 1.32 11.40 +/- 1.17 11.61 +/- 1.53 DR25 Camp Conoy Guard House 13.84 +/- 1.62 14.20 +/- 1.35 12.49 +/- 1.13 12.95 +/- 0.92 DR26 Rt. 234 and Clark's Landing Road 11.76 i 0.73 11.45 i 0.82 10.29 +/- 2.23 10.76 +/- 0.29 DR27 Rt. 231 and Rt.4 12.66 1.52 10.99 1.76 12.03 +/- 2.31 DR28 Taylors Is. Siren #35 14.32 i 1.13 14.70 +/- 0.74 12.20 +/- 2.80 12.96 +/- 0.68 DR29 Taylors Is. Siren #38 15.21 +/- 2.07 15.71 i 0.97 13.00 +/- 1.06 15.51 +/- 0.63 DR31 Cambridge 16.90 1.01 16.96 0.79 15.33 3.54 16.24 +/- 1.60 DR32 Twining Property, Taylors Island 14.34 +/- 1.11 14.55 +/- 0.80 12.07 +/- 4.18 13.29 +/- 0.69 DR33 P. A. Ransome Property 16.39 +/- 0.90 16.41 +/- 0.37 16.23 + 4.29 15.20 +/- 1.36 DR34 Shoreline at Barge Rd. 10.87 +/- 0.91 10.82 +/- 0.97 8.98 +/- 1.33 9.82 i 0.77 OSGDR1 North of OSGSF 19.16 +/- 1.70 20.86 2.08 16.06 0.90 19.12 1.58 OSGDR2 West of OSGSF 17.35 +/- 2.42 18.11 +/-2.17 14.40 1.77 16.51 +/- 1.90

' TLD missing 101

January 1 - December 31, 2003 Docket Nos. 50-317/50-318/72-8 Table E-1 1 Direct Radiation from Resin Storage Area (Results in units of mR/90 days 4 2a)

Site Code Location First Quarter Second Quarter Third Quarter Fourth Quarter RPDR05 North Fence Lower 16.48 +/- 1.31 17.75 +/- 0.74 15.44 +/- 1.81 18.01 +/- 0.76 RPDR06 North Fence Upper 17.21 +/- 1.38 17.74 +/- 1.62 15.87 +/- 2.53 16.93 i 1.27 RPDR07 West Fence Right 23.87 +/- 1.02 31.33 i 2.18 20.96 i 6.28 18.63 i 0.81 RPDR08 West Fence Left 18.31 1.59 18.73 1.13 20.52 7.71 17.39 1.11 RPDR09 South Fence Upper 18.11 0.58 16.34 1.87 16.98 2.42 19.97 1.65 RPDR10 South Fence Lower 22.52 1.40 25.52 1.62 19.31 3.11 21.78 2.05 RPDR11 East Fence Left 18.06 +/- 2.61 21.06 1.93 17.58 5.25 17.29 1.88 RPDR12 East Fence Right 19.73 +/- 1.23 21.49 +/- 2.63 24.81 i 2.55 26.26 + 2.54 102

( I I I { ( I

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