ML101410104

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Annual Radiological Environmental Operating Report: January 1, 2009 - December 31, 2009
ML101410104
Person / Time
Site: Ginna Constellation icon.png
Issue date: 05/14/2010
From:
Constellation Energy Nuclear Group, EDF Development, Ginna
To:
Office of Nuclear Reactor Regulation
References
Download: ML101410104 (64)
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ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT: JANUARY 1, 2009-DECEMBER 31, 2009 MAY 2010 R.E. Ginna Nuclear Power Plant 1503 Lake Road Ontario, New York 14519

January 1 - December 31, 2009 Docket Nos. 50-244 TABLE OF CONTENTS LIST O F FIGU RES .............................................................................................................................. ii LIST O F TA BLES ............................................................................................................................... iii I. SU M M AR Y ....................................................................................................................................... 1 II. R.E. GINNA NUCLEAR POWER PLANT RADIOLOGICAL ENVIRONMENTAL M ON ITO RIN G PRO GRA M ............................................................................................... 2 II.A . INTRO DU CTION ........................................................................................................... 2 II.B. PROGRAM ................................................................ 2 II.B.1 Objectives ............................................................ 2 II.B .2 Sam ple Collection ........................................................................................................ 2 II.B .3 D ata Interpretation ........................................................................................... .... ..3 II.B .4 Program Exceptions ...................................................................................................... 3 II.C . RE SU LTS AN D D ISCU SSION S .......................................................................... .............. 4 II.C .1 A quatic Environm ent ...................................................................................................... 4 II.C .L.a Surface and Drinking W ater ........................................................................................ 4 II.C .1.b A quatic Organism s ...................................................................................................... 5 II.C .1.c Shoreline Sedim ent ...................................................................................................... 5 II.C .2 A tm ospheric Environm ent ............................................................................................. 5 II.C .2.a A ir Particulate Filters ................................................................................................. 5 II.C .2.b A ir Iodine ........................................................................................................................ 6 II.C .3 Terrestrial Environm ent ............................................................................................... 6 II.C .3.a V egetation ....................................................................................................................... 6 II.C .3.b M ilk ................................................................................................................................. 6 II.C .4 D irect Radiation ......................................................................................................... 7 II.C .5 G roundw ater M onitoring W ells ................................................................................... 7 II.D . CON CLU SION .......................................................................................................................... 8 V . REFEREN CES ................................................................................................................................ 11 APPEN D IX A REM P Sam ple Locations .................................................................................... 12 A PPEN D IX B REM P Analytical Results ................................................................................. 21 A PPEN D IX C Quality A ssurance Program ............................................................................... 43 A PPEN D IX D Land U se Survey ............................................................................................... 58 i

January 1 - December 31, 2009 Docket Nos. 50-244 LIST OF FIGURES Figure Title Page A-1 Map of New York State and Lake Ontario Showing Location of R.E. Ginna Nuclear P ower Plan t .............................................................................................................................. 17 A -2 Onsite Sam ple Locations ................................................................................................... 18 A-3 Offsite Sample Locations (TLDs and milk farms within 5 miles) ...................................... 19 A-4 Water Sample, Milk Farms and TLD Locations .................................................................. 20 ii

January 1 - December 31, 2009 Docket Nos. 50-244 LIST OF TABLES Table Title Page 1 Synopsis of 2009 Ginna Nuclear Power Plant Radiological Environmental Monitoring Pro gram ...................................................................................................................................... 9 2 Annual Summary of Radioactivity in the Environs of the Ginna Nuclear Power Plant .......... 10 A-1 Locations of Environmental Sampling Stations for the R.E. Ginna Nuclear Plant ............. 14 B-i Concentration of Tritium, Gamma Emitters and Gross Beta in Surface and Drinking Water ........................................................................................................................................ 23 B-2 Concentration of Gamma Emitters in the Flesh of Edible Fish .......................................... 25 B-3 Concentration of Gamma Emitters in Sediment ................................................................. 26 B-4 Concentration of Iodine-131 in Filtered Air (Charcoal Cartridges) ................... ....27 B-5 Concentration of Beta Emitters in Air Particulates - Onsite Samples ............................... 29 B-6 Concentration of Beta Emitters in Air Particulates - Offsite Samples ............................... 32 B-7 Concentration of Gamma Emitters in Air Particulates ...................................................... 34 B-8 Concentration of Gamma Emitters in Vegetation Samples ............................................... 35 B-9 Concentration of Gamma Emitters (including 1-131) in Milk ............................................ 36 B-10 Typical MDA Ranges for Gamma Spectrometry ............................................................... 37 B-11 Typical LLDs for Gamma Spectrometry ............................................................................. 38 B -12 D irect Radiation ....................................................................................................................... 39 B-13 Groundwater M onitoring Wells .......................................................................................... 42 C-1 Results of Participation in Cross Check Programs ............................................................ 45 C-2 Results of Quality Assurance Program ............................................................................... 48 C-3 Teledyne Brown Engineering's Typical MDAs for Gamma Spectrometry ....................... 57 iii

January 1 - December 31, 2009 Docket Nos. 50-244 I.

SUMMARY

The Annual Radiological Environmental Operating Report is published in accordance with Section 5.0 of the Offsite Dose Calculation Manual, (ODCM). This report describes the Radiological Environmental Monitoring Program, (REMP), and its implementation as required by the ODCM.

The REMP is implemented to measure radioactivity in the aquatic and terrestrial pathways. The aquatic pathways include Lake Ontario fish, Lake Ontario water, and Deer Creek water.

Measurement results of the samples representing these pathways contained only natural background radiation or low concentrations of Cs-137 resulting from past atmospheric nuclear weapons testing. Terrestrial pathways monitored included airborne particulate and radioiodine, milk, food products, and direct radiation. Analysis of terrestrial pathways demonstrated no detectable increase in radiation levels as a result of plant operation. The 2009 results were consistent with data for the past five years and exhibited no adverse trends.

The analytical results from the 2009 Radiological Environmental Monitoring program demonstrate that the operation of the R.E. Ginna Nuclear Power Plant had no measurable radiological impact on the environment. The results also demonstrate that operation of the plant did not result in a measurable radiation dose to the general population above natural background levels.

During 2009, 1283 samples were collected for analysis by gross beta counting and/or gamma spectroscopy. These included 984 air samples, 64 water samples, 16 fish samples, 5 sediment samples, 21 vegetation samples, 38 milk samples, and 155 dosimeter measurements. During 2009 there were ten deviations from the REMP sampling schedule. The minimum number of samples required by the ODCM (Ref. 2) were collected for all pathways.

Samples were collected by R.E. Ginna Nuclear Power Plant's Chemistry personnel and analyzed by the Constellation Energy Ft. Smallwood Environmental Laboratory in Baltimore, Maryland.

A summary of the content of the REMP and the results of the data collected for indicator and control locations are provided in Tables 1 and 2.

I

January 1 - December 31, 2009 Docket Nos. 50-244 II. R. E. GINNA NUCLEAR POWER PLANT RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM II.A. INTRODUCTION The R.E. Ginna Nuclear Power Plant (Ginna) is an operating nuclear generating facility consisting of one pressurized water reactor. Ginna achieved criticality in September 1969 and commenced commercial operation in July 1970. The location of the plant in relation to local metropolitan areas is depicted in Appendix A, Figure A-1.

Results of the monitoring program for the pre-operational and previous operational periods through 2008 have been reported in a series of documents.

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 detectable activity analytical results (Table 2), a compilation of the analytical data (Appendix B), the results of the Quality Assurance Program (Appendix C), and the results of the Land Use Survey (Appendix D). 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 the R.E. Ginna Nuclear Power Plant.

Il.B. PROGRAM II.B.1 Obiectives The objectives of the REMP for the R.E. Ginna Nuclear Power Plant are:

a. Measure and evaluate the effects of plant operation on the environment.
b. Monitor background radiation levels in the environs of the Ginna site.
c. Demonstrate compliance with the environmental conditions and requirements of applicable state and federal regulations, including the ODCM and 40 CFR 190.
d. Provide information by which the general public can evaluate environmental aspects of the operation of R.E. Ginna Nuclear Power Plant.

II.B.2 Sample Collection The locations of the individual sampling stations are listed in Table A-1 and shown in Figures A-2 and A-3. All samples were collected by contractors to, or personnel of Constellation Energy according to R.E. Ginna Nuclear Power Plant procedures.

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January 1 - December 31, 2009 Docket Nos. 50-244 II.B.3 Data Interpretation Many results in environmental monitoring occur at or below the minimum detectable activity (MDA). In this report, all results below the relevant MDA are reported as being "less than" the MDA value. Typical MDA values are listed in Table B-10.

II.B.4 Program Exceptions Ten items reportable in the Annual Environmental Radiological Operating Report under procedure CHA-RETS-VARIATION were reported as follows:

1. February 17, 2009: The air sampler at Environmental Monitoring Station #8 was found off. Power was restored by Rochester Gas and Electric (RG&E). Approximately 343 cubic meters of air were collected by this air sampler during the February 2009 sampling period.
2. March 3, 2009: The air sampler at Environmental Monitoring Station #12 was found off.

The ground fault interrupter (GFI) was successfully reset. Approximately 472 cubic meters of air were collected by this air sampler during the March 2009 sampling period.

3. June 2, 2009: The air sampler at Environmental Monitoring Station #11 was found off.

The GFI was successfully reset. Approximately 323 cubic meters of air were collected by this air sampler during the sampling period.

4. July 10, 2009: The dosimeter at Environmental Monitoring Station #23 was found with moisture in the plastic sleeving. The outer plastic sleeving was found to be damaged and was replaced with a new plastic sleeving.
5. July 14, 2009: The air sampler at Environmental Monitoring Station #6 was found off.

Power to the unit was successful restored. Approximately 429 cubic meters of air was collected by air sampler #6 during the sampling period.

6. July 14, 2009: The air sampler at Environmental Monitoring Station #7 was found off.

Power to the unit was successful restored. Approximately 379 cubic meters of air was collected by air sampler #7 during the sampling period.

7. August 3, 2009: The air sampler at Environmental Monitoring Station #6 was found to have an alternate sampling head and torn particulate filter. Maintenance staff had incorrectly fitted air sampler #6 with a sampling head from an Emergency Response Organization (ERO) air sampler at the same location. Labels were installed on the REMP and ERO air sampler equipment to prevent reoccurrence.
8. August 17, 2009: The air sampler at Environmental Monitoring Station #9 was found off.

The GFI was successfully reset. Approximately 342 cubic meters of air were collected by this air sampler during the sampling period.

9. August 24, 2009: The air sampler at Environmental Monitoring Station #9 was found off.

The sample unit was replaced. Approximately 364 cubic meters of air were collected by this air sampler during the sampling period.

10. October 5, 2009: The dosimeter at Environmental Monitoring Station #31 was missing at the time of collection and suspected to have been removed by vandals during the sampling period. No direct radiation data could be collected at this location for this sampling period.

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January 1 - December 31, 2009 Docket Nos. 50-244 II.C. RESULTS AND DISCUSSIONS All the environmental samples collected during the year were analyzed using Constellation Energy laboratory procedures (Ref. 3). The analytical results for this reporting period are presented in Appendix B and the detectable activity results 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.

II.C.1 Aquatic Environment The aquatic environment surrounding the plant was monitored by analyzing samples of surface and drinking water, aquatic organisms, and shoreline sediment. These samples were obtained from various sampling locations near the plant.

II.C.l.a Surface and Drinking Water Samples are collected weekly from Lake Ontario, upstream (Russell Station or Monroe County Water Authority - Shoremont) and downstream (Ontario Water District Plant - OWD),

composited monthly, and analyzed for gross beta activity (Table B-i). There was no statistically significant difference between the upstream and downstream sample concentrations. The 2009 averages were 2.09 pCi/liter and 2.07 pCi/liter for the upstream and downstream samples, respectively. Gamma isotopic analysis of the monthly composite samples showed no statistically significant difference in activity between the upstream and downstream samples.

Weekly samples are taken from the plant circulating water intake (Circ In) and discharge canal (Circ Out), and composited monthly. The 2009 averages were 2.06 pCi/liter and 2.16 pCi/liter for the intake and discharge canal -respectively. These are essentially the same as the upstream and downstream values as they fall within the + 1 sigma error band and range of the measurement.

Samples of Deer Creek, which transects the site from west to east, are collected and analyzed monthly. The average gross beta concentration seen in the Deer Creek samples was 5.05 PCi/liter. Historically, Deer Creek gross beta values are typically higher than other surface water samples due to Radon progeny in the soils from which the creek recharges and over which the creek flows.

Gamma isotopic analysis including 1-131 is performed on each monthly composite sample.

These are listed in Table B-1 and are separated by source of sample. No anomalous results were noted. The analysis allows the determination of Iodine-131 activity of < 1 pCi/liter. Any positive counts and the 1 sigma error are reported. During 2009, no sample results indicated 1-131 activity in excess of the LLD for the analysis.

Tritium analysis was performed on all water samples on a monthly basis. Composites are made from the weekly samples and a portion filtered to remove interferences for analysis by beta scintillation. During 2009, no sample results indicated tritium activity.

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January 1 - December 31, 2009 Docket Nos. 50-244 II.C.l.b Aquatic Organisms Indicator fish are caught in the vicinity of the Discharge Canal and analyzed for radioactivity from liquid effluent releases from the plant. The fish are filleted to represent that portion which would normally be eaten. Additional fish are caught more than 15 miles away to be used as control samples and are prepared in the same manner.

At a minimum, four different species of fish are analyzed during each half-year from the indicator and background locations. Fish are caught by R.E. Ginna Nuclear Power Plant environmental staff and are analyzed by gamma spectroscopy after being held for periods of less than one week to keep the LLD value for the shorter half-life isotopes realistic. Detection limits could also be affected by small mass samples, (< 2000 grams), in some species. Gamma isotopic concentrations (pCi/kilogram wet) are listed in Table B-2.

During 2009, none of the indicator or control samples indicated gamma activity.

II.C.1.e Shoreline Sediment Samples of shoreline sediment are taken upstream (Town of Greece near Slater Creek) and downstream (Near the Ontario Water District) of R.E. Ginna Nuclear Power Plant.

Results of the gamma isotopic analysis for sediment are included in Table B-3, along with benthic sediment from Lake Ontario. During 2009, there was no indication in the samples of any activity other than naturally occurring radionuclides and trace levels of Cesium-137 consistent with background levels.

II.C.2 Atmospheric Environment Radioactive particles in air are collected by drawing approximately one standard cubic foot per minute (SCFM) through a two inch diameter particulate filter. The volume of air sampled is measured by a dry gas meter and corrected for the pressure drop across the filter. The filters are changed weekly and allowed to decay for three days prior to counting to eliminate most of the natural radioactivity such as the short half-life decay products of radon. The decay period is used to give a more sensitive measurement of long-lived man-made radioactivity.

A ring of six sampling stations is located on the plant site from 150 to 420 meters from the reactor centerline near the point of the maximum annual average ground level concentration, one additional sampling location is located on-site at 690 meters, and two others offsite at approximately 7 miles. In addition, there are three sampling stations located approximately 7 to 16 miles from the site that serve as control stations. See Figure A-2 and Figure A-4.

II.C.2.a Air Particulate Filters Based on weekly comparisons, there was no statistical difference between the Control and Indicator radioactive particulate concentrations. The averages for the control samples (i.e.,

offsite sampling locations) were 0.0228 pCi/m 3 and the averages for the indicators (i.e., onsite 5

January 1 - December 31, 2009 Docket Nos. 50-244 sampling locations) were 0.0230 pCi/m 3 for the period of January to December 2009. Maximum weekly concentrations for all control stations and all indicator stations were 0.041 and 0.041 pCi/m 3 , respectively.

The major airborne species released from the plant are noble gases and tritium. Most of this activity is released in a gaseous form; however, some radioiodine is released as airborne particulate and some of the particulate activity is due to short lived noble gas decay products.

Tables B-5 provides a list of gross beta analysis values for the on-site sample stations. Table B-6 is a list of gross beta analysis values for the off-site sampler stations.

The particulate filters from each sampling location were saved and a 13 week composite was made. A gamma isotopic analysis was performed for each sampling location and corrected for decay. No positive analytical results were found on any sample. The results of these analyses are listed in Tables B-7.

II.C.2.b Air Iodine Radioiodine cartridges are placed at six locations. These cartridges are changed and analyzed each week. No positive analytical results were found on any sample. A list of values for these cartridges is given in Table B-4.

II.C.3 Terrestrial Environment Crops are grown on the plant property in a location with a highest off-site meteorological deposition parameter, and samples of the produce are collected at harvest time for analysis. Control samples are purchased from farms greater than ten miles from the plant.

II.C.3.a Vegetation There was no indication in the vegetation samples of any measurable activity.

Gamma isotopic data is provided in Table B-8.

II.C.3.b Milk There was one indicator dairy herd located within five miles from the plant in 2009. Milk samples are collected monthly during November through May from the indicator farm and biweekly during June through October. A control farm sample is taken for each monthly sample and once during each biweekly period. The milk is analyzed for Iodine- 131 and also analyzed by gamma spectroscopy for major fission products.

All positive counts and the +/-1 sigma error are reported. During 2009, no samples indicated I-131 activity that exceeded the LLD for the analysis.

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January 1 - December 31, 2009 Docket Nos. 50-244 Table B-9 provides a listing of all samples collected during 2009 with analytical results.

II.C.4 Direct Radiation Dosimeters with a sensitivity of 5 millirem/quarter are placed as part of the environmental monitoring program. Thirty-nine dosimeter badges are currently placed in four rings around the plant. These rings range from less than 1,000 feet to 15 miles and have been dispersed to give indications in each of the nine land based sectors around the plant should an excessive release occur from the plant. Badges are changed and read after approximately 3 months exposure.

Direct radiation readings at locations #7 and # 13 are influenced by close proximity to radioactive equipment storage areas and will normally read slightly higher than other locations.

For the year of 2009, on-site exposure ranged between 8.9 - 16.4 mrem/quarter, with an average exposure of 12.5 mrem/quarter and off-site exposure ranged between 8.1 - 15.9 mrem/quarter with an average exposure of 11.2 mrem/quarter.

40 CFR 190 requires that the annual dose equivalent not exceed 25 millirem to the whole body of any member of the public. Comparing the quarterly average of 10.8 millrem observed at the control dosimeter stations as background (equivalent to 43.2 millirem annually) and the highest site boundary dosimeter annual reading (54.9 millirem observed at Station 15) indicates a 11.7 millirem hypothetical maximum direct radiation dose exposure to an offsite member of the public.

Table B-12 provides dosimeter readings at each location for each quarter.

II.C.5 Groundwater Monitoring Wells In accordance with R.E. Ginna Nuclear Power Plant's Chemistry procedures, environmental groundwater monitoring wells are sampled quarterly. There is a total of 9 onsite groundwater monitoring wells:

" Three located adjacent to the All Volatiles Treatment (AVT) Building, screened at 3 depths to include groundwater from top of the water table down to bedrock.

" Three located east of the Screenhouse, screened at 3 depths to include groundwater from top of the water table down to bedrock.

  • One to the west of the Screenhouse.

" One to the southeast of the Contaminated Storage Building (CSB).

" One located south of the Butler Building and upgradient from the reactor containment building, which serves as a control sample point.

Groundwater samples are analyzed for tritium to a detection limit of 500 pCi/L. In 2009, no radioactivity was detected in groundwater samples.

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January 1 - December 31, 2009 Docket Nos. 50-244 Results of the groundwater monitoring well sampling are presented in Table B-13.

II.D. CONCLUSION It is concluded that operation of the R.E. Ginna Nuclear Power Plant produced radioactivity and ambient radiation levels significantly below the limits of the ODCM and 40 CFR 190.

Additionally, there was no significant buildup of plant-related radionuclides in the environment due to the operations of R.E. Ginna Nuclear Power Plant.

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January 1 - December 31, 2009 Docket Nos. 50-244 Table 1 Synopsis of 2009 Ginna Nuclear Power Plant Radiological Environmental Monitoring Program Sample Type Sampling Number of Number Analysis Analysis Number Frequency1 Locations Collected Frequency1 Analyzed Aquatic Environment Surface Water, MC 5 64 Gamma MC 64 Drinking Water Gross Beta MC 64 Bottom Sediment A 1 1 Gamma A 1 Fish 2 A 4 16 Gamma SA 16 Shoreline Sediment SA 2 4 Gamma SA 4 Atmospheric Environment Air Iodine 3 W 6 312 1-131 W 312 4

Air Particulates W 12 624 Gross Beta W 624 Gamma QC 48 Direct Radiation Ambient Radiation Q 39 155 TLD Q 155 Terrestrial Environment Milk 5 M/BW 2 38 Gamma M/BW 38 Vegetation 6 A 8 21 Gamma A 21

' W=Weekly, BW=BiWeekly (15 days), M=Monthly (31 days), Q=Quarterly (92 days), SA=Semiannual, A=Annual, C=Composite 2 Twice during fishing season including at least four species 3 The collection device contains activated charcoal 4 Beta counting is performed >= 24 hours2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br /> following filter change. Gamma spectroscopy performed on quarterly composite of weekly samples 5 Bi-Weekly during growing season.

6 Annual at time of harvest. Samples include broad leaf vegetation 9

January 1 - December 31, 2009 Docket Nos. 50-244 Table 2 Annual Summary of Radioactivity in the Environs of the Ginna Nuclear Power Plant Medium or Type and Total Lower Limit of Indicator Location with Highest Annual Control Locations Pathway Sampled Number of Detection (LLD) Locations Mean Highest Annual Mean (F) / Range 1 Mean (F)/Range (Unit of Analyses (F)/Range' Mean Measurement) Performed Name/Distance 2 &

Direction Atmospheric Environment Air Particulates Gross Beta (624) 0.5 2.3 (468/468) Substation 13 2.4 (52/52) 2.3 (156/156)

(10-2 pCi/im 3) (0.7-4.1) STATION-13 (1.1-3.7) (0.9-4.1) 0.69 km SSW Direct Radiation, Ambient Radiation Dosimeters 12.00 (119/120) Onsite-Utility Pole 13.98 (4/4) 11.58 (36/36)

(mR/91 days) 155 (8.6- 16.4) along West Plant (12.1 - 14.8) (8.9- 14.6)

Fence 2.2 km WSW Aquatic Environment Bottom Sediment Gamma (1) 58 89(1/1) North Sector 89(1/1)

(pCi/kg) Cs-1 37 NORTH 1.07 km N Surface Water, Gross Beta (36) 0.75 2.79 (51/51) Deer Creek - DC 7.13 (12/12) 2.09 (12/12)

Drinking Water (1.31-7.13) 0.26 km ESE (3.58 - 7.13) (1.53 - 2.67)

(pCi/L) 1Mean and range based upon detectable measurements only. Fraction (F) of detectable measurements at specified location is indicated in parentheses 2

From the center point of the containment building 10

January 1 - December 31, 2009 Docket Nos. 50-244 V. REFERENCES (1) R.E. Ginna Nuclear Power Plant, Technical Specification 5.6.2; Annual Radiological Environmental Operating Report.

(2) Offsite Dose Calculation Manual for the R.E. Ginna Nuclear Power Plant.

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

(4) Constellation Energy, "Land Use Survey Around R.E. Ginna Nuclear Power Plant, August 2009."

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January 1 - December 31, 2009 Docket Nos. 50-244 APPENDIX A REMP Sample Locations Summary of Apvendix A Content 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 Ginna are given in Table A-1. Figure A-I shows the location of the R.E. Ginna Nuclear Power Plant in relation to New York State and Lake Ontario. Figures A-2, A-3, and A-4 show the locations of the power plant sampling sites in relation to the plant site at different degrees of detail.

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January 1 - December 31, 2009 Docket Nos. 50-244 TABLE OF CONTENTS - SAMPLING LOCATIONS Table Title Page A-1 Locations of Environmental Sampling Stations for the Ginna Nuclear Power Plant ........ 14 Figure Title Page A-1 Map of New York State and Lake Ontario Showing Location of R.E. Ginna Nuclear P ow er P lant ........................................................................................................................ 17 A -2 O nsite Sam ple Locations ............................................................................................... 18 A-3 Offsite Sample Locations (TLDs and milk farms within 5 miles) ............................... 19 A-4 Water Sample, Milk Farms and TLD Locations ........................................................... 20 13

January 1 - December 31, 2009 Docket Nos. 50-244 TABLE A-i Locations of Environmental Sampling Stations for the R.E. Ginna Nuclear Plant Station Description Distance Direction Meters Miles Sector 2 Manor House Yard 320 0.2 E 3 East Field 420 0.3 ESE 4 East of Training Center Parking Lot 280 0.2 SE 5 Creek Bridge 160 0.1 SSE 6 Main Parking Lot 225 0.1 SW 7 West Fence Line 220 0.1 WSW 8 Seabreeze 19200 11.9 WSW 9 Webster 11400 7.1 SW 10 Walworth 13100 8.1 S 11 Williamson 11500 7.1 ESE 12 Sodus Point 25100 15.6 E 13 Substation 13 690 0.4 SSW 2 Onsite-Manor House Yard 320 0.2 E 3 Onsite-In field approximately 200 ft SE of station #2 420 0.3 ESE 4 Onsite- East of Training Center Parking Lot 280 0.2 SE 5 Onsite-Between creek and plant entry road 160 0.1 SSE 6 Onsite-SW side of plant parking lot 225 0.1 SW 7 Onsite-utility pole along West plant fence 220 0.1 WSW 8 Topper Drive-Irondequoit, Seabreeze Substation #51 19200 11.9 WSW 9 Phillips Road-Webster, intersection with Highway #104, 11400 7.1 SW Substation #74 10 Atlantic Avenue-Walworth, Substation #230 13100 8.1 S 11 W. Main Street-Williamson, Substation #207 11500 7.1 ESE 12 Seaman Avenue-Sodus Point-Off Lake Road by 25100 15.6 E Sewer district, Substation #209 13 Onsite - South of Meteorological Tower 260 0.2 WNW 14 NW comer of field along lake shore 770 0.5 WNW 15 Field access road, west of orchard, approximately 3000' 850 0.5 W West of plant 16 SW Comer of orchard, approximately 3000' West of 900 0.6 WSW plant, approximately 200' North of Lake Road 17 Utility pole in orchard, approximately 75" North of Lake 500 0.3 SSW Road 18 Substation 13A fence, North Side 650 0.4 SSW 19 On NW comer of house 100' East of plant access road 400 0.2 S 20 Approximately 150' West of Ontario Center Road and 680 0.4 SSE I approximately 170' South of Lake Road 14

January 1 - December 31, 2009 Docket Nos. 50-244 TABLE A-1 Locations of Environmental Sampling Stations for the R.E. Ginna Nuclear Plant Station Description Distance Direction Meters Miles Sector 21 North side of Lake Road, approximately 200' East of 600 0.4 SE Ontario Center Road 22 North side of Lake Road, SE, property comer 810 0.5 SE 23 East property line, midway between Lake Road and 680 0.4 ESE Lake shore 24 Lake shore near NE comer of property 630 0.4 E 14350 8.9 WSW 25 Substation #73, Klem Road, adjacent to 897 Klem Road 26 Service Center, Plank Road, West of 250 14800 9.2 SW 14700 9.1 SSW 27 Atlantic Avenue at Knollwood Drive utility pole, North side of road 17700 11.0 SE 28 Substation #193, Marion, behind Stanton Ag. Service, North Main Street 29 Substation #208, Town Line Road (CR- 118), 1000' 13800 8.6 ESE North of Route 104 30 District Office, Sodus, on pole, West side of bldg 20500 12.7 ESE 31 Lake Road, pole 20' North of road, 500' East of Salt 7280 4.5 W Road 32 Woodard Road at County Line Road, pole @ Northwest 6850 4.2 WSW comer.

33 County Line Road at RR tracks, pole approximately 100' 7950 4.9 SW East along tracks 34 Pole at Route 104, Lincoln Road, SW Comer. 6850 4.2 SSW 35 Transmission Right of Way, North of Clevenger Road 7600 4.7 SSW on pole.

36 Substation #205, Route 104, East of Ontario Center 5650 3.5 S Road, North side of fence.

37 Rail Road Avenue, pole at 2048 6000 3.7 SSE 38 Fisher Road at RR Tracks, pole East of road 7070 4.4 SE 39 Seeley Road, Pole South side 100' West of intersection 6630 4.1 ESE with Stony Lonesome Road 40 Lake Road at Stoney Lonesome Road, pole at SE comer 6630 4.1 E Lake Ontario Discharge Plume 2200 1.4 ENE Russell Station 25600 15.9 W Prdc voaf Indicator and background samples of lettuce, apples, tomatoes, and cabbage are collected from gardens grown on company property and purchased from farms >10 miles from the plant.

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January 1 - December 31, 2009 Docket Nos. 50-244 TABLE A-1 Locations of Environmental Sampling Stations for the R.E. Ginna Nuclear Plant Station Description [ Distance Direction Meters Miles Sector Shoremont/MCWA 27160 16.9 W Ontario Water District 2200 1.4 ENE Circ Water Intake 420 0.3 N Circ Water Discharge 130 0.1 NNE Deer Creek 260 0.2 ESE ILake Ontario Discharge Plume [2200 J 1.4 J ENE Russell Station 25600 15.9 W Eaton Farm, Williamson (Indicator) 8 01 J . ESE Schultz Farm, S. Sodus (Control) 21000 13.0 SE 16

January 1 - December 31, 2009 Docket Nos. 50-244 Figure A-1 Map of New York State and Lake Ontario Showing Location of R.E. Ginna Nuclear Power Plant 17

January 1 - December 31, 2009 Docket Nos. 50-244 Figure A-2 Onsite Sample Locations 18

January 1 - December 31, 2009 Docket Nos. 50-244 Figure A-3 Offsite Sample Locations (TLDs and milk farms within 5 miles) 19

January 1 - December 31, 2009 Docket Nos. 50-244 Figure A-4 Water Sample, Milk Farms and TLD Locations 20

January 1 - December 31, 2009 Docket Nos. 50-244 APPENDIX B REMP Analytical Results Summary of Appendix B Content Appendix B is a presentation of the analytical results for the R.E. Ginna Nuclear Power Plant radiological environmental monitoring programs.

21

January 1 - December 31, 2009 Docket Nos. 50-244 TABLE OF CONTENTS - ANALYTICAL RESULTS Table Title Page B-1 Concentration of Tritium, Gamma Emitters and Gross Beta in Surface and Drinking Water. ............................................................................................................................... 23 B-2 Concentration of Gamma Emitters in the Flesh of Edible Fish ............................ 25 B-3 Concentration of Gamma Emitters in Sediment ......................................................... 2.....

6 B-4 Concentration of Iodine- 131 in Filtered Air (Charcoal Cartridges) ............................ 27 B-5 Concentration of Beta Emitters in Air Particulates - Onsite Samples ......................... 29 B-6 Concentration of Beta Emitters in Air Particulates - Offsite Samples ......................... 32 B-7 Concentration of Gamma Emitters in Air Particulates ................................................. 34 B-8 Concentration of Gamma Emitters in Vegetation Samples .......................................... 35 B-9 Concentration of Gamma Emitters (including 1-131) in Milk ...................................... 36 B-10 Typical MDA Ranges for GammaSpectrometry ........................................................ 37 B-11 Typical LLDs for Gamma Spectrometry ................................................................... 38 B -12 D irect R adiation ................................................................................................................. 39 B-113 Groundwater M onitoring W ells .................................................................................... 42 22

January 1 - December 31, 2009 Docket Nos. 50-244 Table B-1 Concentration of Tritium, Gamma Emitters and Gross Beta in Surface and Drinking Water (Results in units of pCiIL +/- 2a)

Sample Code Sample Date Cs-1 37 H-3 Gamma Emitters Gross Beta CIRC-IN Circulating Water Inlet- N 1/20/2009 2.53 +/- 0.61

  • *k 2/17/2009 2.50 +/- 0.53 3/17/2009 *t 2.17 +/- 0.56 4/14/2009 *t 2.22 +/- 0.53 5/12/2009 2.26 +/- 0.56 6/9/2009 2.16 +/- 0.55
  • *t 7/7/2009 1.31 +/- 0.50 8/4/2009 2.33 +/- 0.53 9/1/2009 1.77 +/- 0.52 9/29/2009 1.88 +/- 0.53 10/29/2009 1.91 +/- 0.53 11/24/2009 1.92 +/- 0.54 12/22/2009 1.80 +/- 0.54 CIRC-OUT Circulating Water Outlet - N 1/20/2009
  • 2.02 +/- 0.54 2/17/2009 2.46 +/- 0.53 3/17/2009 2.14 +/- 0.56 4/14/2009 2.91 +/- 0.57 5/12/2009 1.94 +/- 0.53 6/9/2009 2.34 +/- 0.56 7/7/2009 2.39 +/- 0.58 8/4/2009 2.26 +/- 0.53 9/1/2009 1.95 +/- 0.54 9/29/2009 2.01 +/- 0.55 10/29/2009 1.74 +/- 0.53 11/24/2009 1.78 +/- 0.54 12/22/2009 2.09 +/- 0.57 DC Deer Creek - E 1/6/2009 3.67 +/- 0.78 2/10/2009 5.79 +/- 0.74 3/9/2009 4.75 +/- 0.67 4/7/2009 5.08 +/- 0.73 5/4/2009 3.58 +/- 0.75 6/24/2009 5.72 +/- 0.78 7/20/2009 4.57 +/- 0.88 8/17/2009 4.61 +/- 0.93 9/14/2009 3.78 +/- 0.90 10/12/2009 5.26 +/- 0.88 11/4/2009 6.64 +/- 0.88 12/7/2009 7.13 +/- 0.93 23

January 1 - December 31, 2009 Docket Nos. 50-244 Table B-i Concentration of Tritium, Gamma Emitters and Gross Beta in Surface and Drinking Water (Results in units of pCi/L +/- 2a)

Sample Code Sample Date Cs-1 37 H-3 Gamma Emitters Gross Beta MCWA' Monroe County Water/Shoremont, Greece - W 1/20/2009 2.40 +/- 0.58 2/16/2009 1.99 +/- 0.51 3/16/2009 1.64 +/- 0.53 4/13/2009 2.32 +/- 0.54 5/11/2009 1.80 +/- 0.52 6/8/2009 1.70 +/- 0.52 7/6/2009 2.08 +/- 0.55 8/3/2009 2.66 +/- 0.55 8/31/2009 1.99 +/- 0.53 9/28/2009 1.77 +/- 0.53 10/26/2009 2.61 -i/- 0.61 11/23/2009 2.67 +/- 0.60 12/21/2009 1.53 +/- 0.52 OWD Ontario Water District - E 1/20/2009

  • 1.86 +/- 0.57 2/16/2009 2.05 +/- 0.51 3/16/2009 1.72 +/- 0.54 4/13/2009 2.14 +/- 0.53 5/11/2009 2.61 +/- 0.56 6/8/2009 2.81 +/- 0.58 7/6/2009 2.19+/- 0.56 8/3/2009 2.32 +/- 0.52 8/31/2009 1.74 +/- 0.52 9/28/2009 1.59 +/- 0.53 10/26/2009 1.87 +/- 0.53 11/23/2009 2.45 +/- 0.58 12/21/2009 1.52 +/- 0.53 Control Location
  • All Non-Natural Gamma Emitters, including 1-131, and tritium less than MDA.

24

January 1 - December 31, 2009 Docket Nos. 50-244 Table B-2 Concentration of Gamma Emitters in the Flesh of Edible Fish (Results in units of pCi/kg (wet) +/- 2c)

Sample Code Sample Date Sample Type Cs-1 37 Gamma Emitters EAST East Sector 3/26/2009 Rainbow Trout 5/19/2009 White Sucker Fish 10/29/2009 Chinook Salmon GREECE 1 Control 2/24/2009 Smallmouth Bass HAMLIN 1

  • /

Control 5/29/2009 Chinook Salmon 5/29/2009 Lake Trout *k 5/29/2009 Rainbow Trout '*t 10/13/2009 Chinook Salmon '*

10/13/2009 Pike

  • t 10/13/2009 Rainbow Trout 10/13/2009 White Sucker Fish NORTH
  • A North Sector 1/23/2009 Lake Trout 2/26/2009 Smallmouth Bass 10/1/2009 Brown Trout 12/11/2009 Smallmouth Bass 12/16/2009 Carp 1 Control Location
  • All Non-Natural Gamma Emitters <MDA 25

January 1 - December 31, 2009 Docket Nos. 50-244 Table B-3 Concentration of Gamma Emitters in Sediment (Results in units of pCi/kg (wet) +/- 2a)

Sample Code Sample Date Cs-1 37 Gamma Emitters Shoreline EAST East Sector 4/27/2009 8/3/2009

  • k GREECE1 Control 4/27/2009 8/3/2009 Benthic NORTH 11/12/2009 89+/-23

'Control Location

  • All Non-Natural Gamma Emitters <MDA 26

January 1 - December 31, 2009 Docket Nos. 50-244 Table B-4 Concentration of Iodine-131 in Filtered Air (Charcoal Cartridges)

(Results in units of 10-2 pCi/m 3 +/- 2a)

Start Date Stop Date STATION-02 STATION-04 STATION-07 STATION- STATION-09 STATION-I 1 Manor Training West Fence 081 Webster Williamson House Yard Center Line Seabreeze Parking Lot 12/29/2008 1/5/2009 at at* *t *t *t at *t *t 1/5/2009 1/12/2009 *

  • t * *t 1/12/2009 1/19/2009 *t
  • *t 1/19/2009 1/26/2009 *t *t 1/26/2009 2/2/2009 at *t
  • t 2/2/2009 2/9/2009 *t
  • *t 2/9/2009 2/16/2009 *t *t
  • *t 2/16/2009 2/23/2009 at 2/23/2009 3/2/2009 *t *t
  • t
  • t
  • 3/2/2009 3/9/2009 "*

3/9/2009 3/16/2009 *k *t 3/16/2009 3/23/2009

  • t
  • 3/23/2009 3/30/2009
  • t
  • *t 3/30/2009 4/6/2009 4/6/2009 4/13/2009 4/13/2009 4/20/2009 *
  • t 4/20/2009 4/27/2009 *
  • t
  • at 4/27/2009 5/4/2009
  • t 5/4/2009 5/11/2009
  • at 5/11/2009 5/18/2009 *
  • t 5/18/2009 5/25/2009
  • *t 5/25/2009 6/1/2009
  • t 6/1/2009 6/8/2009 *t 6/8/2009 6/15/2009 6/15/2009 6/22/2009 6/22/2009 6/29/2009 6/29/2009 7/6/2009 7/6/2009 7/13/2009
  • 7/13/2009 7/20/2009 7/20/2009 7/27/2009 *k 7/27/2009 8/3/2009 8/3/2009 8/10/2009 8/10/2009 8/17/2009 8/17/2009 8/24/2009 8/24/2009 8/31/2009 *t

'Control Location

  • <MDA (1-131) 27

January 1 - December 31, 2009 Docket Nos. 50-244 Table B-4 Concentration of Iodine-131 in Filtered Air (Charcoal Cartridges)

(Results in units of 10-2 pCi/m3 +/- 2a)

Start Date Stop Date STATION-02 STATION-04 STATION-07 STATION- STATION-09 STATION-i 1 Manor Training West Fence 08' Webster Williamson House Yard Center Line Seabreeze Parking Lot

  • l "* * *
  • 8/31/2009 9/7/2009 9/7/2009 9/14/2009
  • t */ * *
  • 9/14/2009 9/21/2009
  • t * *
  • 9/21/2009 9/28/2009
  • k
  • k * *
  • 9/28/2009 10/5/2009
  • / * * *
  • 10/5/2009 10/12/2009 10/12/2009 10/19/2009 10/19/2009 10/26/2009 *A 10/26/2009 11/2/2009 *k */
  • ~ * *
  • 11/2/2009 11/9/2009 */

11/9/2009 11/16/2009 11/16/2009 11/23/2009 11/23/2009 11/30/2009 11/30/2009 12/7/2009 12/7/2009 12/14/2009 12/14/2009 12/21/2009 12/21/2009 12/28/2009 *t

'Control Location

  • <MDA (1-131) 28

January 1 - December 31, 2009 Docket Nos. 50-244 Table B-5 Concentration of Beta Emitters in Air Particulates - Onsite Samples (Results in units of 10-2 pCi/m 3 +/- 2a Uncertainty)

Start Date Stop Date STATION-02 STATION-03 STATION-04 STATION-05 STATION-06 STATION-07 STATION-13 Manor House East Field Training Creek Bridge Main Parking West Fence Substation 13 Yard Center Parking Lot Line Lot 12/29/2008 1/5/2009 2.8 +/- 0.1 2.9+/- 0.1 3.1 +/-0.2 3.2 +/-0.2 2.9 +/- 0.1 3.0 +/- 0.2 2.9 +/- 0.2 1/5/2009 1/12/2009 2.0 +/- 0.1 2.1 +/-0.1 2.1 +/-0.1 2.4 +/- 0.1 2.2 +/- 0.1 2.1 +/-0.1 2.2 +/- 0.2 1/12/2009 1/19/2009 2.7 +/- 0.1 2.8 +/- 0.1 2.9 +/- 0.1 3.2 +/-0.2 3.0 +/- 0.1 2.9 +/- 0.2 2.9 +/- 0.2 1/19/2009 1/26/2009 3.5 +/- 0.2 3.4 +/- 0.2 3.5 +/- 0.2 3.9 +/- 0.2 3.7 +/- 0.2 3.5 +/- 0.2 3.6 +/- 0.2 1/26/2009 2/2/2009 3.4 +/- 0.1 3.4 +/- 0.1 3.5+/-0.2 3.8 +/- 0.2 3.5 +/- 0.2 3.6 +/-0.2 3.4 +/- 0.2 2/2/2009 2/9/2009 2.6 +/- 0.1 2.8 +/- 0.1 2,7 +/- 0.1 3.2 +/-0.2 2.8 +/- 0.1 2.8 +/- 0.2 3.0 +/-0.2 2/9/2009 2/16/2009 1.9 +/- 0.1 1.9 +/- 0.1 1.9 +/- 0.1 2.1 +/-0.1 2.0 +/- 0.1 1.9 +/- 0.1 1.8 +/- 0.2 2/16/2009 2/23/2009 2.1 +/-0.1 2.1 +/-0.1 2.1 +/-0.1 2.4 +/- 0.1 2.1 +/-0.1 2.0 +/- 0.1 2.3 +/- 0.2 2/23/2009 3/2/2009 2.6 +/- 0.1 2.8 +/- 0.2 2.9 +/- 0.2 3.3 +/-0.2 3.1 +/-0.2 3.1 +/-0.2 3.1 +/-0.2 3/2/2009 3/9/2009 3.0 +/- 0.1 3.2 +/- 0.1 3.0 +/- 0.1 3.4 +/- 0.2 3.1 +/-0.1 3.3 +/- 0.2 3.1 +/-0.2 3/9/2009 3/16/2009 3.0 +/- 0.1 3.2 +/- 0.1 3.1 +/-0.1 3.4 +/- 0.2 3.1 +/-0.1 3.2 +/- 0.2 3.2 +/- 0.2 3/16/2009 3/23/2009 3.2 +/- 0.1 3.1 +/-0.1 3.5 +/- 0.2 3.4 +/-0.2 3.2 +/- 0.2 3.3 +/-0.2 3.4+/-0.2 3/23/2009 3/30/2009 1.9+/-0.1 2.0 +/- 0.1 2.1 +/-0.1 2.3 +/- 0.1 2.1 +/- 0.1 2.0 +/- 0.1 2.1 +/-0.2 3/30/2009 4/6/2009 1.5 +/- 0.1 1.6 +/-0.1 1.8 +/- 0.1 1.7 +/- 0.1 1.7 +/- 0.1 1.8 +/- 0.1 1.7 +/- 0.2 4/6/2009 4/13/2009 1.9+/-0.1 1.9 +/-0.1 2.1 +/-0.1 2.4 +/- 0.1 2.1 +/-0.1 2.1 +/-0.1 2.1 +/-0.2 4/13/2009 4/20/2009 3.0 +/- 0.1 3.3 +/- 0.2 3.5 +/- 0.2 3.5 +/- 0.2 3.4 +/- 0.2 3.3 +/-0.2 3.3 +/- 0.2 4/20/2009 4/27/2009 1.4 +/- 0.1 1.4 +/- 0.1 1.6 +/- 0.1 1.7 +/- 0.1 1.5 +/- 0.1 1.6 +/- 0.1 1.5 +/- 0.2 4/27/2009 5/4/2009 2.1 +/-0.1 2.1 +/-0.1 2.3 +/- 0.1 2.4 +/-0.1 2.2 +/- 0.1 2.2 +/- 0.1 2.3 +/-0.2 5/4/2009 5/11/2009 1.7 +/- 0.1 1.8 +/-0.1 1.9 +/- 0.1 2.0 +/-0.1 1.9 +/- 0.1 1.8 +/- 0.1 2.0 +/-0.2 5/11/2009 5/18/2009 1.9 +/- 0.1 2.0 +/-0.1. 2.2 +/- 0.1 2.0 +/- 0.1 2.1 +/-0.1 2.0 +/- 0.1 2.2 +/- 0.2 5/18/2009 5/25/2009 2.3 +/- 0.1 2.2 +/- 0.1 2.4 +/- 0.1 2.2 +/- 0.1 2.3 +/- 0.1 1.9 +/-0.1 2.5+/-0.2 5/25/2009 6/1/2009 1.0 +/- 0.1 1.0 +/- 0.1 1.1 +/- 0.1 1.0 +/- 0.1 1.1 +/-0.1 1.1 +/-0.1 1.1 +/-0.2 29

January 1 - December 31, 2009 Docket Nos. 50-244 Table B-5 Concentration of Beta Emitters in Air Particulates - Onsite Samples (Results in units of 10-2 pCi/m3 +/- 2a Uncertainty)

Start Date Stop Date STATION-02 STATION-03 STATION-04 STATION-05 STATION-06 STATION-07 STATION- 13 Manor House East Field Training Creek Bridge Main Parking West Fence Substation 13 Yard Center Parking Lot Line Lot 6/1/2009 6/8/2009 1.3 +/- 0.1 1.3 +/- 0.1 1.4 +/- 0.1 1.3 +/- 0.1 1.3 +/- 0.1 1.5 +/- 0.1 1.5 +/- 0.2 6/8/2009 6/15/2009 1.2 +/- 0.1 1.2 +/- 0.1 1.4 +/- 0.1 1.3 +/- 0.1 1.5 +/- 0.1 1.4 +/- 0.1 1.5 +/-0.2 6/15/2009 6/22/2009 1.6 +/- 0.1 1.8 +/- 0.1 1.8 +/- 0.1 1.6 +/- 0.1 1.9 +/- 0.1 2.1 +/-0.1 2.2 +/- 0.2 6/22/2009 6/29/2009 2.0 +/- 0.1 2.1 +/-0.1 2.2 +/- 0.2 2.2 +/- 0.1 2.2+/-0.2 2.4 +/- 0.2 2.5 +/- 0.2 6/29/2009 7/6/2009 1.2 +/-0.1 1.1 +/-0.1 1.2 +/-0.1 1.3 +/- 0.1 1.2 +/- 0.1 1.2 +/- 0.1 1.4 +/- 0.2 7/6/2009 7/13/2009 0.7 +/- 0.1 1.2 +/- 0.1 1.3 +/-0.1 1.1 +/-0.1 1.6 +/- 0.2 1.9 +/- 0.2 2.0+/-0.2 7/13/2009 7/20/2009 1.6+/-0.1 1.6 +/- 0.1 1.7+/-0.1 1.6 +/- 0.1 2.0 +/- 0.2 2.0+/-0.2 1.6 +/- 0.2 7/20/2009 7/27/2009 2.1 +/-0.1 2.0 +/- 0.1 2.0 +/- 0.1 2.2 +/- 0.1 2.2 +/- 0.1 2.2 +/- 0.1 2.4+/-0.2 7/27/2009 8/3/2009 2.3 +/- 0.1 2.3 +/- 0.1 2.5 +/- 0.1 2.3 +/- 0.1 2.5 +/- 0.1 2.5 +/- 0.1 2.6 +/- 0.2 8/3/2009 8/10/2009 2.1 +/-0.1 2.0 +/-0.1 2.0 +/- 0.1 2.0 +/- 0.1 2.1 +/-0.1 2.2 +/- 0.1 2.2+/-0.2 8/10/2009 8/17/2009 4.0+/-0.2 4.0 +/- 0.2 4.1 +/-0.2 3.7 +/- 0.2 4.0 +/- 0.2 3.9+/-0.2 3.7 +/- 0.3 8/17/2009 8/24/2009 2.5 +/- 0.1 3.8 +/- 0.2 2.5 +/- 0.1 2.3 +/- 0.1 2.5 +/- 0.2 2.7+/-0.2 2.4 +/- 0.2 8/24/2009 8/31/2009 1.6 +/-0.1 1.7+/-0.1 1.5 +/- 0.1 1.5 +/- 0.1 1.6 +/- 0.1 1.7+/-0.1 1.7 +/- 0.2 8/31/2009 9/7/2009 2.8 +/- 0.1 2.7 +/- 0.1 2.8 +/- 0.1 2.8 +/- 0.1 2.7 +/- 0.1 3.0 +/- 0.1 3.0 +/- 0.2 9/7/2009 9/14/2009 3.0+/-0.2 3.1 +/-0.2 3.1 +/-0.2 3.1 +/-0.2 3.1 +/-0.2 3.1 +/- 0.2 3.2 +/- 0.3 9/14/2009 9/21/2009 1.9 +/- 0.1 1.9 +/- 0.1 2.0 +/- 0.1 1.8 +/- 0.1 1.9 +/- 0.1 2.0 +/- 0.1 2.4 +/- 0.2 9/21/2009 9/28/2009 2.1 +/-0.1 2.2 +/- 0.1 2.2 +/- 0.1 2.0 +/- 0.1 2.2 +/- 0.1 2.3 +/- 0.1 1.9 +/- 0.2 9/28/2009 10/5/2009 1.0 +/- 0.1 1.2 +/- 0.1 1.3 +/-0.1 1.2 +/- 0.1 1.2 +/- 0.1 1.3 +/- 0.1 1.2 +/- 0.2 10/5/2009 10/12/2009 1.5 +/- 0.1 1.7 +/- 0.1 1.6 +/- 0.1 1.6 +/- 0.1 1.8 +/- 0.1 1.9 +/- 0.1 1.6 +/- 0.2 10/12/2009 10/19/2009 1.5 +/- 0.1 1.6 +/- 0.1 1.7+/-0.1 1.7 +/- 0.1 1.6 +/- 0.1 1.6 +/- 0.1 1.7 +/- 0.2.

10/19/2009 10/26/2009 2.5 +/- 0.1 2.5 +/- 0.1 2.5 +/- 0.1 2.5 +/- 0.1 2.4 +/- 0.1 2.7 +/- 0.1 2.7 +/- 0.2 10/26/2009 11/2/2009 1.4 +/- 0.1 1.5 +/- 0.1 1.6 +/-0.1 1.5 +/-0.1 1.6 +/- 0.1 1.6 +/- 0.1 1.7 +/- 0.2 30

January 1 - December 31, 2009 Docket Nos. 50-244 Table B-5 Concentration of Beta Emitters in Air Particulates - Onsite Samples (Results in units of 10-2 pCi/m 3 +/- 2a Uncertainty)

Start Date Stop Date STATION-02 STATION-03 STATION-04 STATION-05 STATION-06 STATION-07 STATION-13 Manor House East Field Training Creek Bridge Main Parking West Fence Substation 13 Yard Center Parking Lot Line Lot 11/2/2009 11/9/2009 2.5 +/-0.1 2.4 +/-0.1 2.5 +/-0.1 2.3 +/-0.1 2.4 +/-0.1 2.5+/-0.1 2.9+/-0.2 11/9/2009 11/16/2009 2.4+/-0.1 2.3+/-0.1 2.2+/-0.1 2.3+/-0.1 2.3+/-0.1 2.4+/-0.1 2.5+/-0.2 11/16/2009 11/23/2009 3.2+/-0.2 3.1 +1-0.1 3.1 +/-0.1 3.0 +/- 0.1 3.2+/-0.2 3.4+/-0.2 3.4+/-0.3 11/23/2009 11/30/2009 2.6 +/- 0.1 2.6 +/- 0.1 2.4 +/- 0.1 2.6 +/- 0.1 2.7 +/- 0.2 2.9 +/- 0.1 2.8 +/- 0.2 11/30/2009 12/7/2009 2.1 -/- 0.1 2.1 +/-0.1 2.2+/-0.1 2.0+/-0.1 2.4+/-0.1 2.3+/-0.1 2.3+/-0.2 12/7/2009 12/14/2009 3.0 +/- 0.2 3.0 +/- 0.1 2.8 +/- 0.1 3.1 +/- 0.1 3.1 +/- 0.2 3.1 +/- 0.2 3.2 +/- 0.2 12/14/2009 12/21/2009 2.5+/-0.1 2.8+/-0.1 2.6+/-0.1 2.4+/-0.1 2.6+/-0.1 2.5+/-0.1 2.9+/-0.2 12/21/2009 12/28/2009 1.7+/-0.1 1.8+/-0.1 1.7+/-0.1 1.6+/-0.1 1.7+/-0.1 1.8+/-0.1 1.9+1-0.2 31

January 1 - December 31, 2009 Docket Nos. 50-244 Table B-6 Concentration of Beta Emitters in Air Particulates - Offsite Samples (Results in units of 10-2 pCi/m3 +/- 2ar Uncertainty)

Start Date Stop Date STATION- STATION- STATION- STATION- STATION-08' 09 101 11 121 Seabreeze Webster Walworth Williamson Sodus Point 12/29/2008 1/5/2009 2.8 +/- 0.2 2.8+/-0.2 3.0 +/- 0.1 3.0 +/- 0.1 2.9 +/- 0.1 1/5/2009 1/12/2009 2.0 +/- 0.1 2.2+/-0.2 2.2 +/- 0.1 2.1 +/-0.1 2.1 +/-0.1 1/12/2009 1/19/2009 2.6 +/- 0.1 2.6+/-0.2 3.0 +/- 0.1 3.0 +/- 0.1 2.9 +/-0.1 1/19/2009 1/26/2009 3.7+/-0.2 3.6 +/- 0.3 3.8 +/- 0.2 3.6 +/- 0.2 3.6 +/- 0.2 1/26/2009 2/2/2009 3.3 +/- 0.2 3.3 +/- 0.2 3.2 +/- 0.2 3.3 +/- 0.2 3.4 +/- 0.2 2/2/2009 2/9/2009 3.0 +/- 0.2 2.6 +/- 0.2 2.9 +/- 0.1 2.8 +/- 0.1 2.8 +/- 0.1 2/9/2009 2/16/2009 2.3 +/- 0.2 1.6 +/- 0.2 1.8+/-0.1 1.7 +/- 0.1 1.9 +/- 0.1 2/16/2009 2/23/2009 2.1 +/-0.1 2.2 +/- 0.2 2.1 +/-0.1 2.2 +/- 0.1 2.1 +/-0.1 2/23/2009 3/2/2009 2.9 +/- 0.2 3.0+/-0.3 3.2 +/- 0.2 2.9 +/- 0.2 3.1 +/-0.2 3/2/2009 3/9/2009 3.0 +/- 0.2 2.8+/-0.2 2.9 +/- 0.1 2.9 +/- 0.1 3.1 +/-0.1 3/9/2009 3/16/2009 3.4 +/- 0.2 3.3+/-0.2 3.3+/-0.2 3.2 +/- 0.2 2.7 +/- 0.2 3/16/2009 3/23/2009 3.5 +/- 0.2 3.3 +/- 0.2 3.2 +/- 0.2 3.1 +/-0.1 3.2 +/- 0.2 3/23/2009 3/30/2009 2.1 +/-0.1 2.1 +/-0.2 2.1 +/-0.1 2.0 +/- 0.1 1.8 +/- 0.1 3/30/2009 4/6/2009 1.8 +/- 0.1 1.7 +/- 0.2 1.7 +/- 0.1 1.6 +/- 0.1 1.5 +/- 0.1 4/6/2009 4/13/2009 2.4 +/- 0.1 2.2+/-0.2 2.4 +/- 0.1 2.2 +/- 0.1 2.0 +/- 0.1 4/13/2009 4/20/2009 3.2 +/- 0.2 3.1 +/-0.3 3.2 +/- 0.2 3.0 +/- 0.2 3.0 +/- 0.2 4/20/2009 4/27/2009 1.8 +/- 0.1 1.7 +/- 0.2 1.6 +/-0.1 1.5 +/- 0.1 1.5 +/- 0.1 4/27/2009 5/4/2009 2.5 +/- 0.1 2.5 +/- 0.2 2.5 +/-0.1 2.3 +/- 0.1 2.2 +/- 0.1 5/4/2009 5/11/2009 1.9 +/- 0.1 2.0 +/- 0.2 1.9 +/-0.1 1.9 +/- 0.1 1.7 +/- 0.1 5/11/2009 5/18/2009 2.1 +/-0.1 2.4 +/- 0.2 2.3 +/- 0.1 2.1 +/-0.1 2.0 +/- 0.1 5/18/2009 5/25/2009 2.5 +/- 0.1 2.8 +/- 0.2 2.4 +/- 0.1 2.3 +/- 0.1 2.4 +/- 0.1 5/25/2009 6/1/2009 1.3 +/- 0.1 1.3 +/- 0.2 1.3 +/-0.1 1.2 +/- 0.2 1.0 +/- 0.1 6/1/2009 6/8/2009 1.7 +/- 0.1 1.5 +/- 0.1 1.6 +/- 0.1 1.5 +/- 0.1 1.3 +/- 0.1 6/8/2009 6/15/2009 1.4 +/- 0.1 1.6 +/- 0.1 1.4 +/- 0.1 1.5 +/- 0.1 1.4 +/- 0.1 6/15/2009 6/22/2009 2.1 +/-0.1 2.0 +/- 0.1 2.0 +/- 0.1 1.9 +/- 0.1 1.7 +/- 0.1 6/22/2009 6/29/2009 2.2 +/- 0.2 2.3 +/- 0.2 2.3 +/- 0.2 2.2 +/- 0.2 2.1 +/-0.1 6/29/2009 7/6/2009 1.3 +/- 0.1 1.2 +/- 0.1 1.2 +/- 0.1 1.2 +/- 0.1 1.1 +/-0.1 7/6/2009 7/13/2009 0.9 +/- 0.1 1.0 +/- 0.1 1.4 +/- 0.1 1.3 +/- 0.1 1.0 +/- 0.1 7/13/2009 7/20/2009 1.8 +/-0.1 1.8 +/- 0.1 1.8 +/- 0.1 1.7 +/- 0.1 1.6 +/- 0.1 7/20/2009 7/27/2009 2.2 +/- 0.1 2.3 +/- 0.2 2.3 +/- 0.1 2.4 +/- 0.1 2.2 +/- 0.1 7/27/2009 8/3/2009 2.5 +/- 0.2 2.5 +/- 0.2 1.9 +/- 0.1 2.5 +/- 0:1 2.2 +/- 0.1 8/3/2009 8/10/2009 2.3 +/- 0.1 2.3 +/- 0.2 2.1 +/-0.1 2.2 +/- 0.1 2.1 +/-0.1 8/10/2009 8/17/2009 4.1 +/-0.2 3.1 +/-0.2 3.7 +/- 0.2 3.8 +/- 0.2 3.5 +/- 0.2 8/17/2009 8/24/2009 2.8 +/- 0.2 3.0 +/- 0.2 2.3 +/- 0.1 2.5 +/- 0.1 2.3 +/- 0.1 8/24/2009 8/31/2009 1.7 +/- 0.1 1.7 +/- 0.1 1.6 +/- 0.1 1.6 +/- 0.1 1.5 +/- 0.1

' Control Location 32

January 1 - December 31, 2009 Docket Nos. 50-244 Table B-6 Concentration of Beta Emitters in Air Particulates - Offsite Samples (Results in units of 10-2 pCi/M3 +/- 2a Uncertainty)

Start Date Stop Date STATION- STATION- STATION- STATION- STATION-081 09 101 11 12' Seabreeze Webster Walworth Williamson Sodus Point 8/31/2009 9/7/2009 2.9 +/- 0.1 3.0 +/- 0.1 2.7 +/- 0.1 2.9 +/- 0.1 2.6 +/- 0.1 9/7/2009 9/14/2009 3.3+/-0.2 3.0 +/- 0.2 2.8 +/- 0.2 3.1 +/-0.2 2.8 +/- 0.2 9/14/2009 9/21/2009 2.0 +/-0.1 2.0 +/- 0.1 2.1 +/-0.1 2.1 +/-0.1 1.7 +/- 0.1 9/21/2009 9/28/2009 2.3 +/-0.1 2.1 +/-0.1 1.8 +/- 0.1 2.1 +/-0.1 2.0 +/- 0.1 9/28/2009 10/5/2009 1.3 +/- 0.1 1.2 +/- 0.1 1.3 +/- 0.1 1.3 +/- 0.1 1.1 +/-0.1 10/5/2009 10/12/2009 1.7 +/- 0.1 1.5 +/- 0.1 1.6 +/- 0.1 1.6 +/-0.1 1.6 +/- 0.1 10/12/2009 10/19/2009 1.7 +/-0.1 1.6 +/- 0.1 1.7 +/- 0.1 1.7 +/- 0.1 1.4 +/- O.1 10/19/2009 10/26/2009 2.6 +/- 0.1 2.4 +/- 0.1 2.4 +/- 0.1 2.6 +/- 0.1 2.4 +/- 0.1 10/26/2009 11/2/2009 1.6 +/-0.1 1.6 +/- 0.1 1.5 +/- 0.1 1.4 +/- 0.1 1.4 +/- 0.1 11/2/2009 11/9/2009 2.5 +/- 0.1 2.4 +/- 0.1 2.3 +/- 0.1 2.3 +/- 0.1 2.1 +/-0.1 11/9/2009 11/16/2009 2.4 +/- 0.1 2.2 +/- 0.1 2.4 +/- 0.1 2.4 +/- 0.1 2.3 +/- 0.1 11/16/2009 11/23/2009 3.3 +/- 0.2 3.1 +/-0.2 3.3 +/- 0.1 3.1 +/-0.2 3.1 +/-0.1 11/23/2009 11/30/2009 2.8 +/- 0.1 2.6 +/- 0.1 2.9 +/- 0.1 2.7 +/-0.1 2.5 +/- 0.1 11/30/2009 12/7/2009 2.3 +/- 0.1 2.0 +/- 0.1 2.1 +/-0.1 2.2 +/- 0.1 2.2 +/- 0.1 12/7/2009 12/14/2009 3.0 +/- 0.2 2.7 +/- 0.1 3.1 +/-0.1 3.0 +/- 0.1 2.9 +/- 0.1 12/14/2009 12/21/2009 2.5 +/-0.1 2.5 +/- 0.1 2.6 +/- 0.1 2.6 +/- 0.1 2.5 +/- 0.1 12/21/2009 12/28/2009 1.7 +/-0.1 1.6 +/- 0.1 1.8 +/- 0.1 1.7 +/- 0.1 1.7 +/-0.1

'Control LocationI 33

January 1 - December 31, 2009 Docket Nos. 50-244 Table B-7 Concentration of Gamma Emitters in Air Particulates (Results in units of 10-3 pCi/m3 +/- 2a)

Sample Date STATION-02 STATION-03 STATION-04 STATION-05 STATION-06 STATION-07 Manor House Yard East Field Training Center Creek Bridge Main Parking Lot West Fence Line Parking Lot 3/30/2009 * .....

6/29/2009 ......

9/28/2009 ......

12/28/2009 ......

Sample Date STATION-081 STATION-09 STATION-101 STATION-11 STATION-121 STATION-13 Seabreeze Webster Walworth Williamson Sodus Point Substation 13 3/30/2009 ......

6/29/2009 ......

9/28/2009 ......

12/28/2009 * * * * * *

  • All Non-Natural Gamma Emitters <MDA 34

January 1 - December 31, 2009 Docket Nos. 50-244 Table B-8 Concentration of Gamma Emitters in Vegetation Samples (Results in units of pCi/kg (wet) +/- 2ar)

Sample Code Sample Date Sample Type Cs-1 37 Gamma Emitters CONTROL' Local Sites in Control Sectors 7/27/2009 Raspberries 8/13/2009 Greens 8/13/2009 Squash 8/13/2009 Tomato 10/1/2009 Apples 10/1/2009 Grapes EAST East Sector 7/21/2009 Greens 8/18/2009 Tomato ESE East South East Sector 7/15/2009 Raspberries 7/21/2009 Greens 8/13/2009 Squash 8/18/2009 Tomato 10/29/2009 Apples SE South East Garden 9/17/2009 Grapes SOUTH South Garden 9/16/2009 Apples SSE South South East Garden 6/25/2009 Greens *A 8/18/2009 Tomato 9/30/2009 Apples SSW South South West Garden 9/30/2009 Apples

  • SW Intake 9/30/2009 Apples
  • WEST 2 On site West Sector 10/8/2009 Apples
  • 1 Control Location 2 LLD for 1-131 not met due to Long Decay time
  • All Non-Natural Gamma Emitters <MDA 35

January 1 - December 31, 2009 Docket Nos. 50-244 Table B-9 Concentration of Gamma Emitters (including 1-131) in Milk (Results in units of pCi/Liter +/- 2a Sample Code Sample Date Cs-1 37 Gamma Emitters EATON ESE Indicator 1/27/2009 2/24/2009 3/25/2009 4/21/2009 5/19/2009 6/2/2009 6/16/2009 6/30/2009 7/14/2009 7/28/2009 8/11/2009 8/25/2009 9/9/2009 9/22/2009 10/6/2009 10/20/2009 11/3/2009 12/1/2009 12/29/2009 SCHULTZ1 South Sodus Control 1/27/2009 2/24/2009 3/25/2009 4/21/2009 5/19/2009 6/2/2009 6/16/2009 6/30/2009 7/14/2009 7/28/2009 8/11/2009 8/25/2009 9/9/2009 9/22/2009 10/6/2009 10/20/2009 11/3/2009 12/1/2009 12/29/2009 Control Location

  • All Non-Natural Gamma Emitters <MDA 36

January 1 - December 31, 2009 Docket Nos. 50-244 Table B-10 Typical MDA Ranges for Gamma Spectrometry Surface Selected Air Water, Ground Oysters Shoreline Vegetation Nuclides Particulates3 Drinking Fish water Milk(pCi/kg) Sediment Soil (pCi/kg) (pCiIL)

(10.2 pCi/m ) Water (pCi/L)

Na-22 0-.8 2.8-5.8 22.6-48 1.9-6.3 5.3-7.8 23.9-35.1 40.9-65.4 18.1 -91.2 18.8-59.5 K-40 0-9.7 26.5-63.8 220-370 0-0 46.2-62.6 179-295 405.8 - 607.7 163.3-670 163-468 Cr-51 0-7 18.7-39.1 191 -480 12.2-39.2 28.6-41.1 221-384 238-561 84.7-721 99.4-339 Mn-54 0-.7 2.4-5.1 21.5-32.7 1.6-5.3 4-5.8 20.1 -28.9 35.6-52.1 14.7-76 15.2-47.4 Co-58 0-.8 2.4-5.1 22.1 -51.2 1.5-5.2 4-5.8 25.7-32.5 34.1-57 13.5-83.6 15.1 -49.4 Fe-59 0-1.9 5.2-11.1 28-232.1 3.4-10.8 9.7-14.1 62.2-96.8 71.4-136 30.7-205 34.9-115 Co-60 0-.7 2.7-5.6 25.8-40.5 1.8-5.9 4.6-7.4 22.3-34.2 38.7-57.8 17.4-84.7 18.2-56 Zn-65 0-1.4 5.3-11.2 56.9-97.4 4-14.2 10.5-15 47.8-76.9 89.8-140 33.4-209 37.9-119 Nb-95 0-1 2.6-5.4 26.7-67.1 1.8-6.2 4.1 -6.1 32.6-49.7 41.1 -85.1 11.3- 107 15.7-49.7 Zr-95 0-1.4 4.2-8.8 37.6-74.1 2.8-9.1 6.8-10 43.7-54.4 62.1 -101 23.2-142 26.7-80.5 Ru-106 0-5.4 20.9-43.8 133-263 14.2-46 33.5-47.8 179-226 280-368 130-606 123.6-395 Ag-110m 0-.6 2.3-4.8 16.8-30.6 1.5-4.8 3.7 - 5'3 19.3-22.5 29.6-45 12.3-85.2 13.7-43.3 1-131 0-278 0-5 22.2-1136 1.4-5.6 .6-.8 119-1086 54-662 15.7-447 5.5-81.6 Cs-134 0-.6 2.2-4.6 18.4-25.7 1.4-4.8 3.4-5.1 17-23.7 27.1 -52.3 12.5-81 13.1 -42.8 Cs-137 0-.6 2.4-5.2 19.4-30.6 1.6-5.6 3.7-6 19.6-24.6 29-51.4 12-75.3 14.2-47.5 Ba-140 0-6.1 4.1 -9.5 83.8-462 2.5-8.3 5.1 -8.9 71.7-365 16-336 27.3-329 17.6-97 La-140 0-6.1 4.1 -9.5 83.8-462 2.5-8.3 5.1 -8.9 71.7-365 16-336 27.3-329 17.6-97.1 Ce-144 0-1.8 12.1 -24.7 49.8-87.3 8.5-27.8 18.8-27.6 60.4-74.8 135-180 56.9-284 56.3-170

'This MDA range for 1-131 on a silver zeolite cartridge is typically 4.16 x 10,%3 to 3.40 x 10^-2 37

January 1 - December 31, 2009 Docket Nos. 50-244 Table B-11 Typical LLDs for Gamma Spectrometry Selected Water Fish Sediment Particulate* Vegetation Milk Nuclides pCi/I pCi/Kg pCi/Kg 10- 3 pCi/m 3 pCi/Kg pCi/I Na-22 4.1 24 59 3.7 29 6 26 7771277`,3. 6~ 304 Mn-54 3.8 20 49 2.8 24 5 r --

7- - 58 .c319 103 28 50 11 Fs-59 7.8 45 Zn-65 7.9 54 141 7.0 57 12

~

>.IJt N~95~t T~x;<~ -uU 24 Zr-95 65 35 79 5.0 43 8 P 7 R U-'

l 6 6- . . 55 ý- .8 .-

Ag-110m 3.6 15 42 2.2 21 4 FTe712,- h 41 1,70 - -~v 27 -",248 0 1-131 3.2* 13 41 1.9** 19 4*

Cs-137 3.9 17 58 2,8 26 5

__ _ __ _ __ _ _ mLIýss y~7 s t- ~ >

La-140 4.8 19 67 3.9 33 5

  • The LLD for 1-131 measured in drinking water and milk is 0.5 pCi/L
    • The LLD for 1-131 measured on charcoal filter is 9.4 x 10-3 pCi/m 3 38

January 1 - December 31, 2009 Docket Nos. 50-244 Table B-12 Direct Radiation (Results in Units of mR/90 days +/- 2a)

StatioLrc3 io F t.'Second "Thir Fobuth&

I~~~d Qitr Žurr Qurer, Quartbr 2 Onsite-Manor House Yard 12.6 + 1.4 11.5 +4 0.9 14.8 0.9 11.6 + 0.6 3 Onsite-In field approximately 200 ft SE of + 1 12.1 0.9 11.3 1.1 15.4 12.1 + 0.5 station #2 + +

4 Onsite-Training Center yard driveway circle _+

12.7 0.7 11.7 0.9 14.1 0.8 10.8 + 0.5 5 Onsite-Between creek and plant entry road +

13.7 0.9 12.8 0.9 15.9 1.3 12 + 0.8

+ +

6 Onsite-SW side of plant parking lot +{,

10.2 0.9 9.0 0.8 12.4 0.8 8.9 + 0.6

+[ +

7 Onsite-utility pole along West plant fence 14.4 0.9 12.1 1.0 14.6 0.9 14.8 + 0.6

+[

81 Topper Drive-Irondequoit, Seabreeze 11.2 0.9 10.4 0.9 12.8 0.7 10.2 + 0.6 Substation #51 9 Phillips Road-Webster, intersection with Highway#104, Substation #74 11.1 + 0.7 9.7 +/- 0.9 13.4 + 0.7 9.8 + 0.6 10 1 Atlantic Avenue-Walworth, Substation #230 10.2 +/- 1.1 8.9 +/- 0.8 12.7 +/- 0.7 8.9 +/- 0.6 11 W. Main Street-Williamson, Substation #207 11.1 +/- 0.8 9.1 +/- 0.8 13.4 +/- 0.6 9.8 +/- 0.8 12' 12 Seaman Avenue-Sodus Point-Off Lake Road by Sewer district, Substation #209 10.7 + 1.0 10.5 +/- 0.9 14.6 + 0.8 10.5 + 0.6 13 Onsite- South of Meteorological Tower 12.1 +/- 0.8 10.8 +/- 0.8 14.3 +/- 1.0 11 +/- 0.7 14 NW corner of field along lake shore 12.2 +/- 0.9 11.1 +/- 1.0 15.0 +/- 1.3 11.1 +/- 0.7 15 Field access road, west of orchard, 13.6 +/- 0.9 12.7 +/- 0.9 16.4 +/- 0.7 12.2 +/- 0.6 approximately 3000'West of plant 39

January 1 - December 31, 2009 Docket Nos. 50-244 TABLE B-12 (Continued)

Direct Radiation (Results in Units of mR/90 days + 2a)

~'~Loctin~$ ~ ' Firstf ~S6Zodftd Thiiidý Forh I S - Quarter,uatn Ourtn urn 16 SW Corner of orchard, approximately 3000' West of plant, approximately 200' North of 13.0 +/- 0.8 11.8 +/- 0.9 14.2 +/- 0.7 12.3 +/- 0.7 Lake Road 17 Utility pole in orchard, approximately 75" North 12.7 +/- 1.0 11.3 +/- 0.9 14.3 +/- 0.7 10.9 +/- 0.9 of Lake Road 18 Approximately 30' North of NE comer of 10.7 +/- 1.0 9.1 +/- 0.8 12.4 +/- 1.1 9.2 +/- 0.4 Substation 13A fence 19 On NW corner of house 100' East of plant 11.3 +/- 1.4 9.6 +/- 1.0 13.6 +/- 0.6 9.6 +/- 0.6 access road 20 Approximately 150' West of Ontario Center Road and approximately 170' South of Lake 13.2 +/- 0.8 11.2 +/- 0.9 14.4 +/- 0.7 12 +/- 0.7 Road 21 North side of Lake Road, approximately 200' 12.8 +/- 0.8 11.1 +/- 0.9 14.2 +/- 1.1 11.7 +/- 0.7 East of Ontario Center Road 22 North side of Lake Road, SE, property owner 11.9 +/- 0.8 9.7 +/- 0.9 13.7 +/- 0.7 10.1 +/- 0.6 23 East property line, midway between Lake Road and Lake shore 12.9 + 0.7 14.0 +/- 1.3 14.7 +/- 0.7 11.3 + 0.9 24 Lake shore near NE corner of property 12.5 +/- 0.8 11.1 +/- 0.9 14.9 +/- 1.1 12.1 +/- 0.6 25 ' Substation #73, Klein Road, adjacent to 897 11.7 +/- 0.9 9.2 +/- 0.9 13.3 +/- 0.6 9.9 +/- 0.6 Klein Road 26 1 Service Center, Plank Road, West of 250 11.3 -n 0.7 9.3 +/- 0.9 13.6 + 0.8 10.2 +/- 0.5 271* Atlantic Avenue at Knollwood Drive utility pole, ..... ... . .. .. .. .

North side of road 11.:5 +/- U.J lu.u +/- U.0 13.9 +/- LZ 1U.3 +/- U.0 40

January 1 - December 31, 2009 Docket Nos. 50-244 TABLE B-12 (Continued)

Direct Radiation (Results in Units of mR/90 days +/- 2a)

'statioh6t< Loain ~ ~ Frt ~ ~ eoc~ Thirid,- Fourh'~

Quartr d" Quartr ~ Quarter, Quarter>~

28 1 Substation #193, Marion, behind Stanton Ag. 11.3 +/- 0.7 9.6 +/- 0.9 13.1 +/- 0.7 9.7 +/- 0.7 Service, North Main Street 29 1 Substation #208, Town Line Road (CR-118), 10.5 +/- 0.8 9.0 +/- 1.0 13 +/- 0.6 9.7 +/- 0.6 1000' North of Route 104 30 1 District Office, Sodus, on pole, West side of 9.6 +/- 0.6 8.1 +/- 0.8 12.1 +/- 0.6 8.9 +/- 0.5 bldg 31 Lake Road, pole 20' North of road, 500' East of 12.5 +/- 1.2 11.1 +/- 0.9 + 11.5 +/- 0.6 Salt Road 32 Woodard Road at County Line Road, pole @ 11.1 +/- 1.1 9.2 +/- 1.0 12.5 +/- 0.6 9.3 +/- 0.4 BW corner 33 County Line Road at RR tracks, pole 11.6 +/- 1.1 9.1 + 1.0 12.3 +/- 0.6 9.7 +/- 0.8 approximately 100' East along tracks 34 Lincoln Road, pole midway between Ridge 13.4 +/- 1.2 12.0 +/- 1.2 15.9 +/- 0.8 12.1 +/- 0.6 Road and Route 104 35 Transmission Right of Way, North of Clevenger Road on pole 12.5 + 0.8 11.4 + 1.0 15.2 + 1.0 11.7 + 0.6 36 Substation #205, Route 104, East of Ontario 11.9 +/- 0.7 9.8 +/- 0.9 13.1 +/- 0.7 10.2 +/- 1.0 Center Road, North side of fence 37 Rail Road Avenue, pole at 2048 11.0 +/- 0.8 8.6 +/- 0.7 12.4 +/- 0.6 9.6 +/- 0.6 38 Fisher Road at RR Tracks, pole East of road 13.1 + 1.0 10.2 + 0.8 14.6 + 0.7 11.3 + 0.8 39 Seeley Road, Pole South side 100' West of intersection with Stony Lonesome Road 12.6 +/- 1.6 10.6 + 0.9 14.3 + 0.7 10.8 + 0.7 40 Lake Road at Stoney Lonesome Road, pole at SE corner 12.0 _ 0.9 9.1 + 1.1 12.9 + 0.9 9.4 +/- 0.9 1 - Control Location

  • - The Dosimeter was missing at the time of collection and suspected to have been removed by vandals during the sampling period. Accordingly, no direct radiation data could be collected at this location for this sampling period.

41

January 1 - December 31, 2009 Docket Nos. 50-244 TABLE B-13 Groundwater Monitoring Wells

........... .........I.................

Location Sample Date Tritium AVT, S. 13' 03/17/09

  • 06/09/09
  • 09/10/09
  • 12/18/09 1
  • AVT, M. 17' 03/17/09
  • 06/09/09
  • 09/10/09
  • 12/18/09
  • AVT, N. 6' 03/17/09
  • 06/09/09
  • 09/10/09
  • 12/18/09
  • Screen House East, N. 24" 03/17/09
  • 06/09/09*

09/10/09

  • 11/10/09
  • Screen House East, M. 20" 03/17/09
  • 06/09/09
  • 09/10/09
  • 11/10/09*

Screen House East, So. 15.5" 03/17/09

  • 06/09/09
  • 09/10/09
  • 11/10/09*

Screen House West 03/17/09

  • 06/09/09
  • 09/10/09
  • 11/10/09 11/18/09
  • CSB, 24' 03/17/09
  • 06/09/09
  • 09/10/09
  • 12/18/09
  • 42

January 1 - December 31, 2009 Docket Nos. 50-244 APPENDIX C Quality Assurance Program Summary of Appendix C Content:

Appendix C is a summary of Constellation Energy Laboratory's quality assurance program for 2009. 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 MDA's achieved by Teledyne Brown for Gamma Spectroscopy.

All the Constellation Energy Laboratory's results contained in Table C-I generally agree with the intercomparison laboratory's results within the range of +/-2 a of each other. In addition, all but two sets of intercomparison results in the table are in full agreement when they were further evaluated using the NRC Resolution Test Criteria'. The two sets in question were the Ba-133 and Cs-137 resultsi which were part of the April 6, 2009 performance standard obtained from ERA. An investigation into the matter revealed that the discrepancies between the results may have been due to a dilution error in preparing the sample for counting; but more probably were due to errors on the part of ERA in preparing the original standard. The uncertainties for the Constellation Energy Laboratory's results and Analytics' results are +/-2a while the ERA laboratory's uncertainty is based on USEPA guidelines2 .

All the results contained in Table C-2 agree within the range of +/-2 a of each other with their respective Constellation Energy Laboratory original, replicate and/or Teledyne Brown Engineering's split laboratory samples, except for the comparisons of four samples involving Cs-137 results: vegetation samples from Ib3, Ib6, and Ib9 collected 7/27/2009 and a fish sample from Ia5 collected on 8/23/2009.

In all four cases low levels of Cs-137 were observed in one of the results of the comparison set and not observed in the other two. These minor discrepancies, occurring very close to or below the analyses MDA's, are most probably due to counting statistical fluctuations and/or the non-homogeneous nature of the sample-splitting process. 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 43

January 1 - December 31, 2009 Docket Nos. 50-244 TABLE OF CONTENTS - ANALYTICAL RESULTS Table Title Page C-1 Results of Participation in Cross Check Programs, ................................................................. 45 C-2 Results of Quality Assurance Program ................................................................................... 48 C-3 Teledyne Brown Engineering's Typical MDAs for Gamma Spectrometry ............................. 57 44

January 1 - December 31, 2009 Docket Nos. 50-244 TABLE C-1 Results of Participation in Cross Check Programs Sample Sample Type Isotope Reported Cross Check Date and Units Observed Laboratory's Lab Results1 Results1 3/19/09 Milk-pCi/L 1-131 77+/-14 79+/-1 Cs-134 81+/-6 94+/-2 Cs-137 110+/-11 111+/-2 Ce-141 92+/-11 95+/-2 Cr-51 255+/-67 305+/-5 Mn-54 135+/-12 128+/-2 Co-58 123+/-12 119+/-2 Fe-59 108+/-15 100+/-2 Co-60 151+/-10 142+/-2 Zn-65 171+/-23 156+/-3 3/19/09 Charcoal 1-131 87+/-7 80+/-1 Cartridge-pCi 3/19/09 Water-pCi/L Gross 13 212+/-3 203+/-3 3/20/09 Filter-pCi/Filter Gross 13 70+/-2 66+/-1 4/06/09 Water-pCi/L Ba-1 33 32+/-4 53+/-5 Co-60 60+/-4 89+/-9 Cs-134 44+/-3 73+/-7 Cs-1 37 110+/-6 168+/-19 Zn-65 64+/-8 84+/-8 4/06/09 Water-pCi/L 1-131 26+/-5 26+/-6 6/18/09 Water-pCi/L 1-131 83+/-25 88+/-1 Cs-134 119+/-8 126+/-2 Cs-1 37 147+/-13 146+/-2 Ce-141 206+/-21 216+/-4 Co-58 70+/-12 70+/-1 Fe-59 99+/-16 93+/-2 Cr-51 301+/-77 304+/-5 Co-60 250+/-13 237+/-4 Mn-54 102+/-12 104+/-2 Zn-65 141+/-24 133+/-2 See discussion at the beginning of the Appendix.

45

January 1 - December 31, 2009 Docket Nos. 50-244 TABLE C Continued Results of Quality Assurance Program Sample Sample Type Isotope Reported Cross Check Date and Units Observed Laboratory's Lab Results' Results' 6/18/09 Filter-pCi/Filter Ce-141 178+/-9 163+/-3 Cr-51 265+/-48 236+/-4 Cs-134 83+/-5 98+/-2 Cs-137 117+/-9 113+/-2 Mn-54 82+/-7 81+/-1 Fe-59 78+/-11 72+/-1 Zn-65 120+/-15 103+/-2 Co-60 190+/-8 184+/-3 Co-58 51+/-7 54+/-1 8/14/09 Water-pCi/L H-3 1.00 1.09 9/17/09 Filter-pCi/Filter Gross J3 77+/-2 75+/-1 9/21/09 Filter-pCi/Filter Cs-1 34 502+/-14 524+/-183 Cs-137 464+/-17 405+/-101 Zn-65 616+/-35 409+/-151 Co-60 802+/-18 694+/-157 10/05/09 Water-pCi/L 1-131 25+/-6 22+/-4 12/10/09 Charcoal 1-131 121+/-7 94+/-2 Cartridge-pCi 12/10/09 Milk-pCi/L 1-131 96+/-30 87+/-1 Ce-141 195+/-17 202+/-3 Cr-51 523+/-93 548+/-9 Cs-1 34 215+/-8 253+/-4 Cs-1 37 183+/-14 179+/-3 Co-58 194+/-15 211+/-4 Mn-54 177+/-13 178+/-3 Fe-59 187+/-20 178+/-3 Zn-65 369+/-30 345+/-6 Co-60 253+/-12 256+/-4 1 See discussion at the beginning of the Appendix 46

January 1 - December 31, 2009 Docket Nos. 50-244 TABLE C Continued Results of Quality Assurance Program Sample Sample Type Isotope Reported Cross Check Date and Units Observed Laboratory's Lab Results' Results' 12/10/09 Water-pCi/L Gross P3 257+/-3 230+/-4 12/10/09 Filter-pCi/Filter Ce-141 96+/-6 83+/-1 Cr-51 281+/-43 225+/-4 Cs-1 34 90+/-6 104+/-2 Cs-1 37 83+/-7 73+/-1 Co-58 93+/-8 87+/-1 Mn-54 81+/-7 73+/-1 Fe-59 83+/-10 73+/-1 Zn-65 170+/-17 141+/-2 Co-60 111+/-7 105+/-2 1 See discussion at the beginning of the Appendix 47

January 1 - December 31, 2009 Docket Nos. 50-244 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-SFA3 1/5/09 1-131 <MDA <MDA **

Air Iodine-SFA4 1/5/09 1-131 <MDA <MDA **

Air Filter -Al 1/5/09 Beta 3.1+/-0.3 2.9+/-0.3 **

Air Filter -A2 1/5/09 Beta 2.9+/-0.2 3.0+/-0.3 **

Air Filter -A3 1/5/09 Beta 3.4+/-0.3 3.2+/-0.3 **

Air Filter -A4 1/5/09 Beta 2.7+/-0.2 2.7+/-0.2 **

Air Filter -A5 1/5/09 Beta 2.6+/-0.2 2.5+/-0.2. **

Air Filter -SFA1 1/5/09 Beta 2.9+/-0.3 3.1+/-0.3 **

Air Filter -SFA2 1/5/09 Beta 6.0+/-0.5 5.5+/-0.5 **

Air Filter -SFA3 1/5/09 Beta 2.7+/-0.2 2.7+/-0.3 **

Air Filter -SFA4 1/5/09 Beta 2.7+/-0.3 2.7+/-0.2 **

10.2 pCi/m3 Air Filter-Al 2/8/09 Beta 2.9+/-0.3 3.1+/-0.3 **

Air Filter-A2 2/8/09 Beta 2.1+/-0.2 2.0+/-0.2 **

Air Filter-A3 2/8/09 Beta 2.9+/-0.3 3.0+/-0.3 **

Air Filter-A4 2/8/09 Beta 2.4+/-0.3 2.5+/-0.3 Air Filter-A5 2/8/09 Beta 2.4+/-0.2 2.4+/-0.2 **

Air Filter-SFA1 2/8/09 Beta 2.8+/-0.3 2.7+/-0.3 Air Filter-SFA2 2/8/09 Beta 2.7+/-0.3 2.6+/-0.3 **

Air Filter-SFA3 2/8/09 Beta 2.7+/-0.3 2.8+/-0.3 **

Air Filter-SFA4 2/8/09 Beta 2.4+/-0.2 2.8+/-0.3 **

Air Iodine-Al 2/8/09 1-131 <MDA <MDA **

Air Iodine-A2 2/8/09 1-131 <MDA <MDA **

pCi/L Bay Water-Wa2 2/27/09 Gamma <MDA <MDA <MDA 10-2 pCi/m3 Air Filter-Al 3/09/09 Beta 3.7+/-0.3 3.2+/-0.3

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

48

January 1 - December 31, 2009 Docket Nos. 50-244 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-A2 3/9/09 Beta 3.4+/-0.3 3.0+/-0.3 **

Air Filter-A3 3/9/09 Beta 4.7+/-0.4 4.3+/-0.3 **

Air Filter-A4 3/9/09 Beta 3.4+/-0.3 3.2+/-0.3 **

Air Filter-A5 3/9/09 Beta 3.2+/-0.3 2.8+/-0.3 **

Air Filter-SFA1 3/9/09 Beta 3.6+/-0.3 3.3+/-0.3 **

Air Filter-SFA2 3/9/09 Beta 3.9+/-0.3 3.6+/-0.3 **

Air Filter-SFA3 3/9/09 Beta 3.5+/-0.3 3.3+/-0.3 **

Air Filter-SFA4 3/9/09 Beta 3.2+/-0.3 3.3+/-0.3 **

Air Iodine-Al 3/9/09 1-131 <MDA < MDA **

Air Iodine-A2 3/9/09 1-131 < MDA < MDA **

pCi/Kg Oysters-la3 3/25/09 Gamma <MDA <MDA <MDA 3

10-2 pCi/m Air Filter-Al 4/06/09 Beta 1.2+/-0.2 1.4+/-0.2 **

Air Filter-A2 4/06/09 Beta 1.2+/-0.3 1.4+/-0.3 **

Air Filter-A3 4/06/09 Beta 1.5+/-0.3 1.5+/-0.3 **

Air Filter-A4 4/06/09 Beta 1.1+/-0.2 1.2+/-0.2 **

Air Filter-A5 4/06/09 Beta i. 1+/-0.2 1.0+/-0.2 **

Air Filter-SFA1 4/06/09 Beta 1.2+/-0.3 1.4+/-0.3 **

Air Filter-SFA2 4/06/09 Beta 1.5+/-0.3 1.9+/-0.3 **

Air Filter-SFA3 4/06/09 Beta 1.0+/-0.2 1.3+/-0.2 **

Air Filter-SFA4 4/06/09 Beta 1.1+/-0.2 1.3+/-0.2 **

10-2 pCi/m3 Air Iodine-A4 4/06/09 1-131 <MDA <MDA **

Air Iodine-A5 4/06/09 1-131 <MDA <MDA **

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

49

January 1 - December 31, 2009 Docket Nos. 50-244 TABLE C Continued 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 Filters-Al 4/15/09 Gamma <MDA <MDA <MDA Air Filters-A2 4/15/09 Gamma <MDA <MDA <MDA Air Filters-A3 4/15/09 Gamma <MDA <MDA <MDA Air Filters-A4 4/15/09 Gamma <MDA <MDA <MDA Air Filters-A5 4/15/09 Gamma <MDA <MDA <MDA Air Filters-SFA1 4/15/09 Gamma <MDA <MDA <MDA Air Filters-SFA2 4/15/09 Gamma <MDA <MDA <MDA Air Filters-SFA3 4/15/09 Gamma <MDA <MDA <MDA Air Filters-SFA4 4/15/09 Gamma <MDA <MDA <MDA 102 pCi/m3 Air Iodine-Al 5/04/09 1-131 <MDA <MDA Air Iodine-A2 5/04/09 1-131 <MDA <MDA Air Filter-Al 5/04/09 Beta 1.3+/-0.2 1.6+/-0.2 Air Filter-A2 5/04/09 Beta 1.3+/-0.2 1.4+/-0.2 Air Filter-A3 5/04/09 Beta 1.5+/-0.2 1.6+/-0.2 Air Filter-A4 5/04/09 Beta 2.2+/-0.4 2.6+/-0.4 Air Filter-A5 5/04/09 Beta 1.9+/-0.2 2.0+/-0.2 Air Filter-SFA1 5/04/09 Beta 1.9+/-0.3 1.9+/-0.3 **

Air Filter-SFA2 5/04/09 Beta 2.0+/-0.3 2.0+/-0.3 Air Filter-SFA3 5/04/09 Beta 2.5+/-0.3 2.5+/-0.3 Air Filter-SFA4 5/04/09 Beta 1.9+/-0.3 1.9+/-0.3 pCi/Kg Soil-SFSI 5/24/09 Gamma <MDA <MDA <MDA Soil-SFS5 5/24/09 Cs-1 37 191+/-47 239+/-44 239+/-72 Vegetation- 5/24/09 Gamma <MDA <MDA <MDA SFB1 Vegetation- 5/24/09 Gamma <MDA <MDA

<MDA SFB5

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

50

January 1 - December 31, 2009 Docket Nos. 50-244 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 5/29/09 Gamma MDA MDA MDA 3

10-2 pCi/m Air Iodine-SFA2 6/8/09 1-131 <MDA <MDA Air Iodine-SFA3 6/8/09 1-131 <MDA <MDA 10-2 pCi/m3 Air Filter-Al 6/8/09 Beta 1.0+/-0.2 1.0+/-0.2 Air Filter-A2 6/8/09 Beta 1.1+/-0.2 1.1+/-0.2 Air Filter-A3 6/8/09 Beta 1.0+/-0.2 1.0+/-0.2 Air Filter-A4 6/8/09 Beta 1.5+/-0.2 1.5+/-0.3 Air Filter-A5 6/8/09 Beta 1.6+/-0.2 1.5+/-0.2 Air Filter-SFA1 6/8/09 Beta 1.7+/-0.3 1.7+/-0.3 Air Filter-SFA2 6/8/09 Beta 1.4+/-0.3 1.3+/-0.3 Air Filter-SFA3 6/8/09 Beta 1.3+/-0.2 1.3+/-0.3 Air Filter-SFA4 6/8/09 Beta 1.2+/-0.2 1.1+/-0.2 **

pCi/Kg Oysters-la3 6/25/09 Gamma <MDA <MDA <MDA pCi/Kg Shoreline Wbl 6/30/09 Gamma <MDA <MDA <MDA mR/90 Days DR05 7/01/09 TLD 14.38+/-2.02 13.82+/-1.72 DR06 7/01/09 TLD 12.74+/-1.81 13.34+/-1.33 **

DR07 7/01/09 TLD 12.64+/-0.51 13.38+/-0.39 **

DR08 7/01/09 TLD 17.58+/-1.66 19.91+/-1.08 **

DR09 7/01/09 TLD 13.71+/-0.96 14.25+/-1.99 **

DR10 7/01/09 TLD 12.55+/-0.98 13.85+/-0.86 **

DR11 7/01/09 TLD 12.41+/-0.76 12.05+/-1.28 **

SFDR14 7/01/09 TLD 18.20+/-2.58 20.33+/-1.39 **

SFDR15 7/01/09 TLD 22.16+/-4.31 24.85+/-4.72 **

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

51

January 1 - December 31, 2009 Docket Nos. 50-244 TABLE C Continued Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split And Location Date Analysis Analysis Analysis Analysis mR/90 Days DR29 7/01/09 TLD 17.33+/-1.63 17.22+/-0.86 **

DR31 7/01/09 TLD 18.26+/-0.74 17.87+/-1.23 **

3 10-2 pCi/m Air Filter-Al 7/06/09 Beta 1.6+/-0.3 1.7+/-0.3 **

Air Filter-A3 7/06/09 Beta 1.6+/-0.3 1.8+/-0.3 **

Air Filter-A4 7/06/09 Beta 1.8+/-0.3 2.1+/-0.3 **

Air Filter-A5 7/06/09 Beta 2.2+/-0.3 1.8+/-0.3 **

Air Filter-SFA1 7/06/09 Beta 2.1+/-0.3 1.8+/-0.3 **

Air Filter-SFA2 7/06/09 Beta 1.9+/-0.3 1.3+/-0.2 **

Air Filter-SFA3 7/06/09 Beta 1.7+/-0.3 2.0+/-0.4 **

Air Filter-SFA4 7/06/09 Beta 1.8+/-0.3 1.4+/-0.3 **

Air Iodine-Al 7/02/09 1-131 <MDA <MDA **

Air Iodine-SFA1 7/02/09 1-131 <MDA <MDA **

pCi/kg Vegetation-IbIl 7/27/09 Gamma <MDA <MDA <MDA Vegetation-lb3 7/27/09 Cs-137 10+/-7 <MDA <MDA Vegetation-lb4 7/27/09 Gamma <MDA <MDA <MDA Vegetation-lb6 7/27/09 Cs-137 <MDA 12+/-9 <MDA Vegetation-lb7 7/27/09 Gamma <MDA <MDA <MDA Vegetation-lb9 7/27/09 Cs-137 <MDA 7+/-6 <MDA 3

10-2 pCi/m Air Filter-Al 8/10/09 Beta 2.6+/-0.3 2.4+/-0.3 **

Air Filter-A2 8/10/09 Beta 1.9+/-0.2 1.8+/-0.2 **

Air Filter-A3 8/10/09 Beta 2.2+/-0.3 2.2+/-0.2 **

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

52

January 1 - December 31, 2009 Docket Nos. 50-244 TABLE C Continued 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 Filter-A4 8/10/09 Beta 2.6+/-0.3 2.9+/-0.3 **

Air Filter-A5 8/10/09 Beta 5.3+/-0.5 5.8+/-0.5 **

Air Filter-SFA1 8/10/09 Beta 3.6+/-0.4 3.9+/-0.4 **

Air Filter-SFA2 8/10/09 Beta 3.0+/-0.3 3.2+/-0.3 **

Air Filter-SFA3 8/10/09 Beta 2.5+/-0.2 3.0+/-0.3 **

Air Filter-SFA4 8/10/09 Beta 2.5+/-0.3 2.6+/-0.3 **

3 10-2 pCi/m Air Iodine-Al 8/06/09 1-131 <MDA <MDA **

Air Iodine-A5 8/06/09 1-131 <MDA <MDA **

pCi/kg Fish-la51 8/23/09 Gamma <MDA 14+/-6 <MDA Vegetation-lbl 8/24/09 Gamma <MDA <MDA <MDA Vegetation-lb4 8/24/09 Gamma 29+/-19 51+/-25 67+/-14 Vegetation-lb8 8/24/09 Gamma <MDA <MDA <MDA pCi/L Bay Water-Wa2 8/31/09 Gamma <MDA <MDA **

3 10-2 pCi/m Air Iodine-A3 9/04/09 1-131 <MDA <MDA **

Air Iodine-A4 9/04/09 1-131 <MDA <MDA **

Air Filter-Al 10/05/09 Beta 1.9+/-0.2 1.8+/-0.2 **

Air Filter-A2 10/05/09 Beta 1.5+/-0.2 1.5+/-0.2 **

Air Filter-A3 10/05/09 Beta 1.9+/-0.2 1.8+/-0.2 **

Air Filter-A4 10/05/09 Beta 2.9+/-0.3 2.9+/-0.3 **

Air Filter-A5 10/05/09 Beta 1.9+/-0.2 1.9+/-0.2 **

Air Filter-SFA1 10/05/09 Beta 2.4+/-0.3 2.5+/-0.3 **

Air Filter-SFA2 10/05/09 Beta 2.3+/-0.2 2.2+/-0.2 **

Air Filter-SFA3 10/05/09 Beta 3.4+/-0.4 3.6+/-0.4 **

Air Filter-SFA4 10/05/09 Beta 2.1+/-0.2 2.1+/-0.2 **

1 See Discussion at beginning of Appendix 53

January 1 - December 31, 2009 Docket Nos. 50-244 TABLE C Continued Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split And Location Date Analysis Analysis Analysis Analysis 3

10-3 pCi/m Air Filters-Al 9/14/09 Gamma <MDA <MDA <MDA Air Filters-A2 9/14/09 Gamma <MDA <MDA <MDA Air Filters-A3 9/14/09 Gamma <MDA <MDA <MDA Air Filters-A4 9/14/09 Gamma <MDA <MDA <MDA Air Filters-A5 9/14/09 Gamma <MDA <MDA <MDA Air Filters-SFA1 9/14/09 Gamma <MDA <MDA <MDA Air Filters-SFA2 9/14/09 Gamma <MDA <MDA <MDA Air Filters-SFA3 9/14/09 Gamma <MDA <MDA <MDA Air Filters-SFA4 9/14/09 Gamma <MDA <MDA <MDA 3

10-2 pCi/m Air Iodine-Al 10/08/09 1-131 <MDA <MDA **

Air Iodine-A2 10/08/09 1-131 <MDA <MDA **

3 10-2 pCi/m Air Filter-Al 10/19/09 Beta 1.7+/-0.2 1.7+/-0.2 **

Air Filter-A2 10/19/09 Beta 1.2+/-0.2 1.2+/-0.2 **

Air Filter-A3 10/19/09 Beta 1.4+/-0.2 1.3+/-0.2 **

Air Filter-A4 10/19/09 Beta 2.1+/-0.3 2.2+/-0.4 **

Air Filter-A5 10/19/09 Beta 1.3+/-0.2 1.3+/-0.2 **

Air Filter-SFA1 10/19/09 Beta 1.9+/-0.3 2.1+/-0.4 **

Air Filter-SFA2 10/19/09 Beta 1.9+/-0.3 2.0+/-0.3 **

Air Filter-SFA3 10/19/09 Beta 3.3+/-0.6 3.5+/-0.6 **

Air Filter-SFA4 10/19/09 Beta 1.9+/-0.3 1.8+/-0.3 **

mR/90 Days DR05 10/01/09 TLD 12.14+/-1.06 13.39+/-0.80 **

DR06 10/01/09 TLD 10.24+/-0.66 11.66+/-1.20 **

DR07 10/01/09 TLD 10.41+/-1.31 11.47+/-1.19 **

DR08 10/01/09 TLD 14.98+/-1.31 16.62+/-1.34 **

DR09 10/01/09 TLD 11.11+/-1.23 13.41+/-0.93 **

DR10 10/01/09 TLD 10.42+/-0.97 11.12+/-2.30 DR11 10/01/09 TLD 10.69+/-1.55 11.04+/-1.75 **

SFDR14 10/01/09 TLD 16.72+/-1.50 15.74+/-2.50 **

SFDR15 10/01/09 TLD 20.72+/-4.62 22.37+/-4.98 **

54

January 1 - December 31, 2009 Docket Nos. 5 0-244 TABLE C Continued Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split And Location Date Analysis Analysis Analysis Analysis mR/90 Days DR29 10/01/09 TLD 15.01+/-0.71 15.08+/-1.92 **

DR31 10/01/09 TLD 15.56+/-1.38 16.36+/-1.88 **

pCi/Kg Bottom **

10/29/09 Cs-1 37 279+/-57 346+/-72 Sediment Wbs2 3

10.2 pCi/m Air Filter-Al 11/08/09 Beta 2.6+/-0.3 2.5+/-0.3 Air Filter-A2 11/08/09 Beta 2.1+/-0.3 2.2+/-0.3 Air Filter-A3 11/08/09 Beta 2.9+/-0.4 2.8+/-0.4 **

Air Filter-A4 11/08/09 Beta 4.1+/-0.5 4.2+/-0.5 **

Air Filter-A5 11/08/09 Beta 2.2+/-0.3 2.3+/-0.2 **

Air Filter-SFA1 11/08/09 Beta 2.8+/-0.4 3.1+/-0.4 Air Filter-SFA2 11/08/09 Beta 2.6+/-0.3 2.7+/-0.3 Air Filter-SFA3 11/08/09 Beta 8.8+/-1.1 9.4+/-1.2 **

Air Filter-SFA4 11/08/09 Beta 2.7+/-0.4 2.5+/-0.4 3

10-2 pCi/m Air Iodine-A3 11/06/09 1-131 <MDA <MDA **

Air Iodine-A5 11/06/09 1-131 <MDA <MDA pCi/L Bay Water-Wa2 11/30/09 Gamma <MDA <MDA <MDA pCi/Kg Vegetation- 11/30/09 Gamma <MDA <MDA <MDA SFB2 Vegetation- <MDA <MDA 11/30/09 Gamma <MDA SFB5 Soil-SFS2 11/30/09 Cs-1 37 104+/-39 57+/-41 88+/-57 Soil-SFS5 11/30/09 Cs-1 37 301+/-60 271+/-43 329+/-54 55

January 1 - December 31, 2009 Docket Nos. 50-244 TABLE C Continued 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 Filter-Al 12/07/09 Beta 1.8+/-0.2 1.5+/-0.2 **

Air Filter-A2 12/07/09 Beta 1.4+/-0.2 1.7+/-0.2 **

Air Filter-A4 12/07/09 Beta 3.7+/-0.6 3.9+/-0.6 **

Air Filter-A5 12/07/09 Beta 1.6+/-0.2 1.5+/-0.2 Air Filter-SFA1 12/07/09 Beta 1.3+/-0.2 1.5+/-0.2 **

Air Filter-SFA2 12/07/09 Beta 2.0+/-0.3 2.1+/-0.3 **

Air Filter-SFA3 12/07/09 Beta 1.9+/-0.2 1.9+/-0.2 **

Air Filter-SFA4 12/07/09 Beta 1.6+/-0.3 1.5+/-0.2 **

3 10-2 pCi/m Air Iodine-Al 12/03/09 1-131 <MDA <MDA. **

Air Iodine-A2 12/03/09 1-131 <MDA <MDA **

pCi/L Bay Water- 12/31/09 Gamma <MDA <MDA Wa2

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

56

January 1 - December 31, 2009 Docket Nos. 50-244 TABLE C-3 Teledyne Brown Engineering's Typical MDAs for Gamma Spectrometry Selected Bay Water Fish Shellfish Sediment Vegetation Particulates Nuclides pCi/I pCi/kg pCi/kg pCi/kg pCi/kg 10- 3pCi/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 57

January 1 - December 31, 2009 Docket Nos. 50-244 APPENDIX D Land Use Survey Summary of Appendix D Content:

Appendix D contains the results of a Land Use Survey conducted around R.E. Ginna 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.

58

January 1 - December 31, 2009 Docket Nos. 50-244 APPENDIX D Land Use Survey Discussion A Land Use Survey was conducted to identify the location of the nearest milk animal, the nearest residence, and the nearest garden greater than 50 square meters in each of the nine sectors within a 5-mile radius of the power plant. A detailed description of the Land Use Survey is given in a separate document (Ref. 4). The position of the nearest residence and garden and animals producing milk for human consumption in each sector is provided in Table D-1.

,7 Table D-1 Land Use Survey Distances Sector Distance to Nearest Distance to Nearest Distance to Milk Residence Garden Producing Animals E 1170 m 580 m N/A Onsite Supplemental Garden ESE 1660 m 390 m N/A Onsite Garden SE 570 m N/A 8270 m SSE 610 m 620 N/A Onsite Supplemental Garden S 1500 m N/A N/A SSW 620 m N/A N/A SW 740 m N/A N/A WSW 1470 m N/A N/A W 2420 m N/A N/A The closest residence is situated in the SE sector (570 meters from the power plant), the nearest garden is in the ESE sector (390 meters), and the nearest milk producing animals was in the SE sector (8,270 meters).

Changes from Previous Years:

The following land use changes have occurred over the within a 5-mile radius of the power plant:

m Some homes/buildings were demolished on R.E. Ginna Nuclear Power Plant property in late 2008/early 2009.

59

January 1 - December 31, 2009 Docket Nos. 50-244

" Distances to all "nearest residences" were reevaluated and re-measured in all sectors using improved mapping and measurement techniques (handheld Global Positioning System (GPS) and Google Earth software). Distances were found to be different from the previous reporting years, with the revised directions and distances noted in the above table. Condition Report No. CR-2009-007273 was issued to document this change in the site's Corrective Action Process.

" The pace of the development of single family homes has slowed compared to previous years.

" No new agricultural land use was identified.

" No new food producing facilities were identified.

Milk Animal Locations:

The milk animal location with a 5-mile radius of the power plant are as follows:

" Eaton Farm -- 6747 Salmon Creek Road, Williamson, NY

" No new milk producing animals were identified in the 2009 Census.

60

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