ML061380543

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2005 Annual Radiological Environmental Operating Report for the R.E. Ginna Nuclear Power Plant
ML061380543
Person / Time
Site: Ginna Constellation icon.png
Issue date: 04/30/2006
From: Barnett A, Bartal L, Jones G
Constellation Generation Group
To:
Office of Nuclear Reactor Regulation
References
Download: ML061380543 (58)
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ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT FOR THE R. E. GINNA NUCLEAR POWER PLANT January 1 - December 31, 2005 A. M. Barnett L. J. Bartal, Ph.D.

G. C. Jones l

CONSTELLATION ENERGY CONSTELLATION GENERATION GROUP, LLC APRIL 2006

January 1 - December 31, 2005 Docket No. 50-244 TABLE OF CONTENTS LIST OF FIGURES ................................................................... ii LIST OF TABLES ................................................................... iii I.

SUMMARY

.................................................................... 1 II. R. E. GINNA NUCLEAR POWER PLANT RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM .................................................................... 2 I.A. INTRODUCTION 2 H.B. PROGRAM 2 l.B. 1 Obiectives 2 II.B.2 Sample Collection 2 II.B.3 Data Interpretation 3 ll.B.4 Proeram Exceptions 3 I.C. RESULTS AND DISCUSSIONS 3 II.C.1 Aquatic Environment 3 H.C.l.a Surface and Drinking Water 3 JJ.C.L.b Aquatic Organisms 4 II.C.1.c Shoreline Sediment 4 II.C.2 Atmospheric Environment 5 H.C.2.a Air Particulate Filters 5 II.C.2.b Air Iodine 6 II.C.3 Terrestrial Environment 6 II.C.3.a Vegetation 6 II.C.3.b Milk 6 fl.C.4 Direct Radiation 6 ll.D. CONCLUSION 7 IV. REFERENCES ..................................... 10 APPENDIX A Sample Locations for the REMP .. 11...................

APPENDIX B Analysis Results for the REMP .. ................................. 20 APPENDIX C Ouality Assurance Program .. .................................. 40 APPENDIX D Land Use Survev .................................... . 54 i

January 1 - December 31, 2005 Docket No. 50-244 LIST OF FIGURES Figure Title Page A-1 Map of New York State and Lake Ontario Showing Location of the R. E. Ginna Nuclear Power Plant ................................................................ 16 A-2 Onsite Sample Locations ................................................................ 17 A-3 Offsite Sample Locations (TLDs and milk farms within 5 miles) ........................................... 18 A4 Water Sample, Milk Farms and TLD Locations ................................................................ 19 ii

January 1 - December 31, 2005 Docket No. 50-244 LIST OF TABLES Table Title Page A-I Locations of Environmental Sampling Stations for the R.E. Ginna Nuclear Power Plant . 13 B-1 Concentration of Tritium, Gamma Emitters and Gross Beta in Surface and Drinking Water .21 B-2 Concentration of Gamma Emitters in the Flesh of Edible Fish .23 B-3 Concentration of Gamma Emitters in Sediment .24 B-4 Concentration of Iodine-131 in Filtered Air (Charcoal Cartridges ........................................... 25 B-5a Concentration of Beta Emitters in Air Particulates - Onsite Samples . .....................................

27 B-6a Concentration of Beta Emitters in Air Particulates - Offsite Samples . ....................................

29 B-7 Concentration of Gamma Emitters in Air Particulates ......................................... 31 B-8 Concentration of Gamma Emitters in Vegetation Samples ......................................... 32 B-9 Concentration of Gamma Emitters (including I-131) in Milk ......................................... 33 B-1I Typical MDA Ranges for Gamma Spectrometry ......................................... 35 B-i Typical l LLDs for Gamma Spectometry ......................................... 36 B-12 Direct Radiation ........................................ 37 C-1 Results of Participation in Cross Check Programs ....................................... 41 C-2 Results of Quality Assurance Program ................................. 45 C-3 Teledyne Brown Engineering's Typical MDAs for Gamma Spectrometry ............................. 53 iii

January 1 - December 31, 2005 Docket No. 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 2005 results were consistent with data for the past five years and exhibited no adverse trends.

The analytical results from the 2005 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 2005, 1228 samples were collected for analysis by gross beta counting and/or gamma spectroscopy. These included 936 air samples, 60 water samples, 16 fish samples, 5 sediment samples, 12 vegetation samples, 43 milk samples, and 156 thermoluminescent dosimeter measurements. During 2005 there were no deviations from the sampling schedule for air samples. The minimum number of samples required in the ODCM (Ref.

2) were collected for all pathways.

Samples were collected by Ginna Station chemistry personnel and analyzed by Constellation Energy Fort Smallwood Environmental Laboratory. A summary of the content of the REMP and the results of all the data collected for indicator and control locations is given in Table 1 and Table 2.

1

January 1 - December 31, 2005 Docket No. 50-244 II. R. E. GINNA NUCLEAR POWER PLANT RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM II.A. INTRODUCTION The R. E. Ginna site is an operating nuclear generating station consisting of one pressurized water reactor. Unit 1 achieved criticality in 1969 and commenced commercial operation in 1970.

The location of the plant in relation to local metropolitan areas is shown on Figure A-1.

Results of the monitoring program for the pre-operational and previous operational periods through 2004 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 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.

II.B. PROGRAM ll.B.1 Objectives The objectives of the REMP for the 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 the R.E. Ginna Nuclear Power Plant.

II.B.2 Sample Collection The locations of the individual sampling stations are listed in Table A-I and shown in Figures A-2 and A-3. All samples were collected by contractors to, or personnel of Constellation Energy according to Ginna Procedures (Ref. 3).

2

January 1 - December 31, 2005 Docket No. 50-244 lI.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.

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

1. Environmental Air Sampler #6 found OOS 1/12/05. Run time 119.6 hours6.944444e-5 days <br />0.00167 hours <br />9.920635e-6 weeks <br />2.283e-6 months <br />, sample volume 514 in3 . Breaker reset, no subsequent failures.
2. Environmental Air Sampler #12 found OOS 10/10/05. Run time 95.5 hours5.787037e-5 days <br />0.00139 hours <br />8.267196e-6 weeks <br />1.9025e-6 months <br />, sample volume 344.8 M3 . Cause was RG&E maintenance, no subsequent failures.
3. Operator of Gerber Milk Farm, Boston Road, no longer produces milk for human consumption as of 10/12/05.

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., Circulating Water, Aquatic Organisms, etc., for the Aquatic Environment).

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 on Lake Ontario and Deer Creek near the plant.

ll.C. L.a Surface and Drinking Water Samples are collected weekly from Lake Ontario, upstream (Monroe County Water Authority -

Shoremont Station) and downstream (Ontario Water District Plant - OWD), composited monthly, and analyzed for gross beta activity, Table B-1. There was no statistically significant difference between the upstream and downstream sample concentrations. The 2005 averages were 2.24 pCi/liter and 2.23 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.

Gross beta peaks of up tolO pCi/liter can occur when the lake is stirred up by wind and the weekly sample includes large quantities of suspended silt.

3

January 1 - December 31, 2005 Docket No. 50-244 Weekly samples are taken from the plant circulating water intake (Circ In) and discharge canal (Circ Out), and composited monthly. The 2005 averages were 2.39 pCi/liter and 2.18 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.

Results for all water beta analyses are listed in Table B-1.

Samples of the creek which crosses the site are collected and analyzed monthly.

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 I-131 is performed on each monthly composite sample. These are listed in Table B- I 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 2005, 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. Tritium data is given in Table B-1.

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.

Four different species of fish are analyzed during each half-year from the indicator and control locations if they are available. There was no statistically significant difference in the activity of the fish caught between the indicator and control 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.

IIC. 1.c Shoreline Sediment Samples of shoreline sediment are taken upstream (Russell Station or Monroe County Water Authority - Shoremont) and downstream (Ontario Water District) of Ginna Station.

Results of the gamma isotopic analysis for sediment are included in Table B-3, along with benthic sediment and cladaphora from Lake Ontario.

4

January 1 - December 31, 2005 Docket No. 50-244 II.C.2 Atmospheric Environment Radioactive particles in air are collected by drawing approximately one 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 6 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, 1 more is located near site at 690 meters, and 2 others offsite at approximately 7 miles. In addition, there are 3 sampling stations located approximately 7 to 16 miles from the site that serve as control stations. See Figures A-2 and A-4.

ll.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 were 0.019 pCi/M3 , and the averages for the indicators were 0.019 pCi/m 3 for the period of January to December, 2005. Maximum weekly concentrations for each station were less than 0.040 pCi/M3 .

The major airborne species released from the plant are noble gases, tritium and radioiodines.

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.

Table B-5a is a list of gross beta analysis values for the on-site sample stations. Table B-6a 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. The results of these analyses are listed in Table B-7.

5

January 1 - December 31, 2005 Docket No. 50-244 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, (Gro-Moore Farm Market in Henrietta, New York).

III.C.3.a Vegetation There was no indication in the samples of any measurable activity other than naturally occurring K-40 and Ra-226.

Gamma isotopic data is given in Table B-8.

II.C.3.b Milk There were two indicator dairy herds located three to five miles from the plant on 1/1/04. The owner of previous indicator farm C retired early in 2002, and a change to the ODCM was submitted to reflect this. Milk samples are collected monthly during November through May from one of the indicator farms and biweekly during June through October from each. Farm B ceased commercial milk production in October 2005, and a change to the ODCM will be submitted to reflect this. No other milk farm is operated within 5 miles of the plant. 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 2005, no samples indicated I-13 1 activity that exceeded the LLD for the analysis.

Table B-9 is a listing of all samples collected during 2005 with analytical results.

IR.C.4 Direct Radiation Thermoluminescent dosimeters, (TLD's), with a sensitivity of 5 millirem/quarter are placed as part of the environmental monitoring program. Thirty-nine TLD badges are currently placed in four rings around the plant. These rings range from less than 1000 feet to 15 miles and have been dispersed to give indications in each of the nine land based sectors around the plant should 6

January 1 - December 31, 2005 Docket No. 50-244 an excessive release occur from the plant. Badges are changed and read after approximately 3 months exposure.

TLD 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 2005, on-site exposure ranged between 9.3 - 17.3 mrem/quarter, with an average exposure of 12.0 mrem/qu-arter and off-site exposure ranged between 9.0 - 13.4 mrem/quarter with an average exposure of 10.9 mrem/quarter.

40 CFR 190 requires that the annual dose equivalent not exceed 25 millirems to the whole body of any member of the public. Using the annual average of control TLD stations as background and the highest site boundary TLD, leads to 5.2 millirem direct radiation dose to the hypothetical maximally exposed member of the public, off-site.

Table B-12 gives TLD readings for each quarter.

II.D. CONCLUSION It is concluded that the operation of R. E. Ginna Nuclear Power Plant 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 Ginna Station.

7

January 1 - December 31, 2005 Docket No. 50-244 Table 1 Synopsis of 2005 R. E. Ginna Nuclear Power Plant Radiological Environmental Monitoring Program Number of Number Analysis Sample Type Sampling Frequency' Locations Collected Analysis Frequency' Number Analyzed Aquatic Environment Drinking Water MC 1 12 Gamma M 12 Gross Beta M 12 Tritium QC 4 Surface Water MC 2 24 Gamma M 24 Gross Beta M 24 Tritium QC 8 Fish2 SA 8 16 Gamma B 16 Sediment SA 2 4 Gamma SA 4 Atmospheric Environment Air Iodine3 W 6 312 Gamma W 312 Air Particulates4 W 12 624 Gross Beta W 624 Gamma Q 52 Milk BM (June thru October) 3 31 Gamma BM 40 M (November thru May) 2 12 Gamma M 14 Direct Radiation Ambient Radiation Q 39 156 TLD Q  ?

Terrestrial Environment Food Products5 A 4 12 Gamma A 10 1 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 2 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 Annually during growing season. Samples include broad leaf vegetation 8

January 1 - December 31, 2005 Docket No. 50-244 Table 2 Annual Summary of Radioactivity in the Environs of the R. E. Ginna Nuclear Power Plant Location with Type and Total Highest Annual Control Number of Average Lower Mean Highest Annual Locations Medium or Pathway Sampled (Unit of Analyses Limit of Detection Indicator Locations Name/Distance & Mean Mean Measurement) Performed (LLD) Mean (F)/Rangel Direction 2 (F)/Rangel (F)/Rangel Aquatic Environment Ontario Water Drinking Water (pCi/L) Gross Beta 0.60 2.23(12/12) District 2.23(12/12) 2.24(12/12)

(1.77 - 2.98) Station 15 (1.77 - 2.98) (1.65 - 2.75) 2.2 km ENE Circulating Water Surface Water (pCi/L) H-3 710 <LLD (36/36) Inlet <LLD (12/12)

Station 15 0.42 km N Gross Beta 0.60 3.26(36/36) Deer Creek 5.24(12/12) 2.24(12/12)

(1.42 - 9.55) Station 18 (3.24 - 9.55) (1.65 - 2.75)

Atmospheric Environment Air Particulates (10-2 pCi/M 3) Gross Beta 0.5 1.85(468/468) Seabreeze 1.95(52/52) 1.85(156/156)

(0.33 - 3.97) Station 8 (0.50 - 3.97) (0.45 - 3.97) 19.2 km WSW Direct Radiation Ambient Radiation (mR/91 days) TLD (468) 11.6 (120/120) West Fence Line 15.4(12/12) 10.7(36/36)

(9.0- 17.3) Station 7 (13.7 - 17.3) (9.0- 12.3) 0.22 km WSW 1 Mean and range based upon detectable measurements only. Fraction (F) of detectable measurements at specified location is indicated in parentheses 2 From the centerpoint of the containment building 9

January 1 - December 31, 2005 Docket No. 50-244 V. REFERENCES (1) R. E. Ginna Nuclear Power Plant, Nos. DPR-XX, 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 2004."

10

January 1 - December 31, 2005 Docket No. 50-244 APPENDIX A Sample Locations for the REMP 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 Ginna Station 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.

11

January 1 - December 31, 2005 Docket No. 50-244 TABLE OF CONTENTS - SAMPLING LOCATIONS Table Title Page A-1 Locations of Environmental Sampling Stations for the R.E. Ginna Nuclear Power Plant ...... 13 Figure Title Page A-1 Map of New York State and Lake Ontario Showing Location of the R. E. Ginna Nuclear Power Plant ................................................................ 16 A-2 Onsite Sample Locations ............................................................... 17 A-3 Offsite Sample Locations (TLDs and milk farms within 5 miles) ........................................... 18 A-4 Water Sample, Milk Farms and TLD Locations ................................................................ 19 12

January 1 - December 31, 2005 Docket No. 50-244 TABLE A-1 Locations of Environmental Sampling Stations for the R. E. Ginna Nuclear Plant Station 1 Description Distance [ Direction

- Meters Miles Sector

<~Air Samplers%-

2 Manor House Yard 320 0.2 E 3 East Field 420 0.3 ESE 4 Training Center Parking Lot 250 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

'Diret adiati'n, 2 Onsite-Manor House Yard 320 0.2 E 3 Onsite-In field approximately 200 ft SE of station 420 0.3 ESE 4 Onsite-Training Center yard driveway circle 250 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 19200 11.9 WSW 9 Phillips Road-Webster, intersection with Highway 11400 7.1 SW

  1. 104, Substation #74 10 Atlantic Avenue-Walworth, Substation #230 13100 8.1 S 11 W. Main Street-Williamson, Substation #207 11500 7.1 ESE 12 1 12 Seaman Avenue-Sodus Point-Off Lake Road by 25100 15.6 E Sewer district, Substation #209 13 At corner of plant-controlled area fence and dogleg 230 0.1 WNW to West 14 NW corner of field along lake shore 770 0.5 WNW 15 Field access road, west of orchard, approximately 850 0.5 W l

_An__ Wert nfnlnt 16 SW Corner of orchard, approximately 3000' West 900 0.6 WSW of plant, approximately 200' North of Lake Road 17 Utility pole in orchard, approximately 75" North of 500 0.3 SSW Lake Road 18 Approximately 30' North of NE corner of 650 0.4 SSW Substation 13A fence 19 On NW corner of house 100' East of plant access 400 0.2 S road 20 Approximately 150' West of Ontario Center Road 680 0.4 SSE and approximately 170' South of Lake Road .

21 North side of Lake Road, approximately 200' East 600 0.4 SE of Ontario Center Road I 13

January 1 - December 31, 2005 Docket No. 50-244 Station Description Distance Direction Meters Miles Sector 22 North side of Lake Road, SE, property owner 810 0.5 SE 23 East property line, midway between Lake Road 680 0.4 ESE and Lake shore 24 Lake shore near NE corner of property 630 0.4 E 25l Substation #73, Klein Road, adjacent to 897 Klein 14350 8.9 WSW Road 26l Service Center, Plank Road, West of 250 14800 9.2 SW 27 ' Atlantic Avenue at Knollwood Drive utility pole, 14700 9.1 SSW North side of road 28 1 Substation #193, Marion, behind Stanton Ag. 17700 11.0 SE Service, North Main Street 29 ' Substation #208, Town Line Road (CR-1 18), 1000 13800 8.6 ESE

.__ ' North of Route 104 30 1 District Office, Sodus, on pole, West side of bldg 20500 12.7 ESE 31 Lake Road, pole 20' North of road, 500' East of 7280 4.5 W Salt Road 32 Woodard Road at County Line Road, pole @ BW 6850 4.2 WSW corner 33 County Line Road at RR tracks, pole 7950 4.9 SW approximately 100' East along tracks 34 Lincoln Road, pole midway between Ridge Road 6850 4.2 SSW and Route 104 SSW 35 Transmission Right of Way, North of Clevenger 7600 4.7 SSW Road on pole SSW 36 Substation #205, Route 104, East of Ontario 5650 3.5 S Center 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 6630 4.1 ESE intersection with Stony Lonesome Road 40 Lake Road at Stoney Lonesome Road, pole at SE 6630 4.1 E corner -

25 Lake Ontario Discharge Plume 2200 1.4 ENE 26 Russell Station 25600 15.9 W 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.

14 Shoremont/MCWA 27160 16.7 15 Ontario Water District 2200 1.4 ENE 16 Circ Water Intake 420 0.3 N 17 Circ Water Discharge 130 0.1 NNE 18 Deer Creek 260 0.2 ESE 25 Lake Ontario Discharge Plume 2200 1.4 ENE 26 Russell Station _ _25600 115.9 14

January 1 - December 31, 2005 Docket No. 50-244 Station Description Distance Direction Meters Miles Sector 21 Farm A 8270 5.1 ESE 22 Farm B 4680 2.9 WSW 24 Farm D 21000 1_13.0 _ _SE 15

January 1 - December 31, 2005 Docket No. 50-244 FIGURE A-1 Map of New York State and Lake Ontario Showing Location of R. E. Ginna Nuclear Power Plant 16

January 1 - December 31, 2005 Docket No. 5 0-244 FIGURE A-2 Onsite Sample Locations

,at Z . I .I Key Gusu0 SfttkMstructur" 17 .- (3\ .-

January 1 - December 31, 2005 Docket No. 50-244 FIGURE A-3 Offsite Sample Locations (TLDs and milk farms within 5 miles)

IFI atin5Mil Permet OV2- Area i I dst "rm TL[)s l l 18

January 1 - December 31, 2005 Docket No. 50-244 FIGURE A-4 Water Sample, Milk Farms and TLD Locations 19

January 1 - December 31, 2005 Docket No. 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 .21 B-2 Concentration of Gamma Emitters in the Flesh of Edible Fish .23 B-3 Concentration of Gamma Emitters in Sediment .24 B-4 Concentration of Iodine-131 in Filtered Air (Charcoal Cartridges) .25 B-5a Concentration of Beta Emitters in Air Particulates - Onsite Samples ...................................... 27 B-6a Concentration of Beta Emitters in Air Particulates - Offsite Samples ..................................... 29 B-7 Concentration of Gamma Emitters in Air Particulates ..................................................... 31 B-8 Concentration of Gamma Emitters in Vegetation Samples ..................................................... 32 B-9 Concentration of Gamma Emitters (including I-13 1) in Milk ................................................. 33 B-10 Typical MDA Ranges for Gamma Spectrometry ..................................................... 35 B-Il Typical LLDs for Gamma Spectrometry ..................................................... 36 B-12 Direct Radiation ..................................................... 37 20

January 1 - December 31, 2005 Docket No. 50-244 Table B-1 Concentration of Tritium, Gamma Emitters and Gross Beta in Surface and Drinking Water (Results in units of pCi/L +/- 2c)

Locatiori Sample H-3 I ;Gamma Gross Beta Date - Emitters Monroe Count Waer  : 01i31/205 -*

  • 2.53:+/- 0.53 IAuthority (MCWA)

Station 14 02/28/2005 *

  • 2.46 0.53

-031820056 i *

  • 2 0.-2 050/2/2005 *
  • 2.06 +/- 0.52 05/31/)2005 *  ; 2.18+/- 0.53 06/27/2005 *
  • 1.67 +/- 0.49 o---l/2005s
  • 1.65 +/- 0.51 08/29/2005 *
  • 1.97 +/- 0.55 0/03120050
  • 2.04 +/- 0.52 10/31/2005 *
  • 2.46+/- 0.53

/28/200 .5 4 01/03/2006 *

  • 2.75 0.57 Ontario Water District 01/31/2005 *
  • 2.08 +/- 0.50 (OWD) ton 2/___ ___28/2005 * --

1.88t 0.52 03/28/2005 *

  • 2.33+/- 0.51 2-5/0 2-0025 * * .5.

05/31/2005 *

  • 1.77 0.50 06.7027/2005  ;
  • 2.34+/-052 08/01/2005 *
  • 1.99 0.54 0/29/2005 *
  • 1.78+/- 0.54 10/03/2005 *
  • 2.55 0.54 1 0/3 005 *-

11/28/2005 *

  • 2.98 0.56 r7...F-'.rr 0-1703/2006 2I15+/-0.54 Cir i Ilet( irc 01/31/2005 3.68 0.61 I)

Station 16 02/28/2005 *

  • 2.16 +/- 0.53 F0 - . 03/30/2005 2 05 05/02/2005 *
  • 1.98 +/- 0.51 r:7<-t "T-<'-05/3hi/20d5--* -* 2-§ r 06/27/2005 *
  • 2.38 i 0.53

/07i1/2075 i . 1:

.95+/-.54 08/29/2005 *

  • 2.21 0.56

.10 2005- * .68d0.55' 10/31/2005 *

  • 2.67 i 0.54 21

January 1 - December 31, 2005 Docket No. 50-244 O*

-11129/2005 , .1.57 0.53 01/03/2006 *

  • 2.47+/-t 0.57 Table B-1 (Continued)

Locabion Sample H-3 Gamma GrossBeta Date Emitters Circulating Water Outlet 01/312005 -* 2.64+/-0. 4 (Circ Out)

Station 17 02/28/2005 *

  • 2.53 +/- 0.55 0 ,8-2005 *- -2. 3 - -0.52 05/02/2005 *
  • 2.08 i 0.51 77- - 05/3112005 - 20 0.1 06/27/2005 *
  • 1.95+/- 0.51

-777o.-2o-5 - 1.42 0.52 08/29/2005 *

  • 2.14+/- 0.55 F

~ ~ ~ ~ 10/31/200~5 10/31/2005 *

  • 22005 2.29 i 0.52 11/28/2005 . ^*.2 53 01/03/2006 *
  • 2.15 0.54 F-.,-.

Deer Creek 01/17/2005 *

  • 4.85 +/- 0.69

'itoni6i8 - , 40 5 20.70' -0 432 03/14/2005 *

  • 3.99 i 0.67

, _ 7 3.51+/-0.65 05/23/2005 *

  • 3.24 +/- 0.70 F ,..68 3 54.07t 07/22/2005 *
  • 9.55 + 1.30

/.8I15I2005 -* ': " 4'73 ' 0.8' 09/19/2005 *

  • 7.29 +/- 1.16

--/67/200.5

"- - * * ' +/-0. 5 11/14/2005 *

  • 5.96 +/- 0.77 A 4 _7 i=.-t F; .-- -.f . - -- -  ; n .. - - - - - _- -¢ - . --
  • All Non-Natural Gamma Emitters, including 1-131, and tritium <MDA 22

January 1 - December 31, 2005 Docket No. 50-244 Table B-2 Concentration of Gamma Emitters in the Flesh of Edible Fish (Results in units of pCi/kg (wet) +/- 2a)

" IAnfit "6An ~

n__ ' ~1 I ~ MMA~ :Fh Tvne -amma Emitters Date Lake Ontario Discharge Plume 1/14/2005 Lake Trout *

(Indicator) btation225 -125 2005-- - Smal(t ssh0a:. .

1/25/2005 Burbot *

-t;- -oo5- -- -Rainbow rou -

08/31/2005 Lake Trout *

./22/2005 .rp .

isi:

9/22/2005 Salmon Fish

  • 10i1/2-00 10> Trown tro*it Russel Station (Control) 1/25/2005 Carp *

.sta~tio 26 ?r77z747 w /-/200h 6/8/2005 Yellow Perch *

.. .71 5/20dS .. thSker:

9/27/2005 Carp Fish

  • 9/27/2005 Pike Fish *
  • A' M6 ' .-ai ,G_-M-_E b5 ' 'E - rwF_ -rt,'9k - !t-
  • AINn- atura Gani Emitter~s <MDA 23

January 1 - December 31, 2005 Docket No. 50-244 Table B-3 Concentration of Gamma Emitters in Sediment (Results in units of pCi/kg (wet) + 2a)

Descnption' Samnple '- ama'Eitters Date Shoreline Sediment Russel Station Station 26 05/16/2005

  • Ontari[oLake obischarge 7 -Of.5/T1i205---

'Plume'Station25 07/22/2005 *

[Beithic medirnent is Eh -a r'>e .I -: ,0:;-

,0 7 ,.-- -,
.=C-<:

ILke Ont~ano Plume Station 25 iscae *:;,,--6i14JO05?t6i *-- -- -

  • All Non-Natural Gamma Emitters <MDA 24

January 1 - December 31, 2005 Docket No. 50-244 Table B-4 Cartridges)

Concentration of lodine-131 in Filtered Air (Charcoal (Results in units of 10.2 pCi/M + 2a) 3

- -SaoSt 7S in-taon- t n .tto

[$ttbte - top ae #8 (C) #9 (I) #11 (1)

  1. 2 (1) #4 (1)- #7 (1)

West Seabreeze Webster Williamson Manor Training Center House Fence Yad Paing Lot -Line fi2/2r12s '01103/20 5 *

  • 01/10/2005 *-

01/03/2006 ,-

11026@7-* M 4 * *

  • 01/24/2005
  • 01/17/2005 F6124J005 011 1/2005 . *-_.

41 02/07/2005 02/14/2005

  • 02/28/2005
  • 02/22/2005 02/28/2005 03/07/2005 * *:

~07I~b0 -!03/14/~ * *

  • 03/14/2005 03/21/2005 I. h " 2005 O32/006  ;;--=*0X00 04/04/2005 04/11/2005
  • j 04/2512005
  • 04/18/2005 05/16/2005
  • 05/09/2005 05/23/2005 05/31//2005 05/3112005 060/6/2005 06/13/2005 06/20/200 5 *
  • L Contr Iocionl  :
  • <MDA (1-131) 25

January 1 - December 31, 2005 Docket No. 50-244 Table B-4 (Continued)

Concentration of lodine-131 in Filtered Air (Charcoal Cartridges)

(Results in units of 10.2 pCi/m 3 i 2a)

[t ~irt Date Stop bat - Statio

  1. 2l -

'Statation

  1. 4)  ::#7 ()

affon

  1. 8 (C)

S'ation

  1. 9 ()

Station

  1. 11 (I)

Manor Training Center West Seabreeze' Webster Williamson House Fence YLaed a king L.t:-t.. ne.. ..

ne ..

L /27/2io25"-9'-;065 -tW'5/20 9 *- -

  • t r* **^ *- -6 07/05/2005 07/11/2005 * * * * *
  • Fb7/1~ 5 - 7f180<05 * * *-st,-'_ * * *_

07/18/2005 07/25/2005 * * * * *

  • F aii2005 0t0tt . -*  :-
  • 0 '-0 iX'~""* ' '~'"<~'

08/08/2005 08/15/2005 * * * * * *

[fl0/~1 /2OS bt72/2OOi 20* <>i -t^ t'*-*0*-'

08/22/2005 08/29/2005 * * * * *

  • 08/29/2005 09/06/2005 * * * * * *

[F)~ei2 ~ 0Ot. 09/12005 - * .. * * *

  • 09/12/2005 09/19/2005 * * * * * *

[7bii/29005 9/26 2005. ^7. . T; . *7 09/26/2005 10/03/2005 * * * * *

  • 10/03/2005 10/10/2005 * * *

[q010aO500§ f 0 0 -S 0 S*-

10/17/2005 10/24/2005 * * * * *

  • D 8 Voo5t~t1'0 3/2005>t -§*- > wt+< t ~rtg 11/07/2005 11i/14/2005*.** -***

11/212005 11/28/2005 * *

  • 11/28/2005 12/05/2005 * * * * *
  • f 11/1tJ20O5 11/2/2005 -

12/12/2005 12/19/2005 * *

  • 12/26/2005 01/03/2006 * * *
  • L _ve~~~~~e S te~~~~~ 7-att 7"~wr7Yo 7a7 ~S

~F~i rT<6wm vNf~Nt t777 tW' a---/Xa-tt-s..-ty7_..................................................

L "ir _fgAdaY 7~eZ-> .............................................. ~s^>~~~ ;d0t 26

January 1 - December 31, 2005 Docket No. 50-244 START STOP Station #2 (I) Station #3 (I) Station #4 (I) Station #5 (I) Station #6 (I) Station #7 (I) Station #13 (1)

DATE DATE Manor House Yard East Field Training Center Creek Bridge Main Parking Lot West Fence Line Substation 13 Parking Lot 12127/2004 1/3/2005 0.0240 +/- 0.0080 0.0270 +/- 0.0080 0.0230 +/- 0.0100 0.0250 +/- 0.0040 0.0260 +/- 0.0030 0.0220 +/- 0.0060 0.0250 +/- 0.0060 1/312005 1/10/2005 0.0120 +/- 0.0060 0.0140 +/- 0.0060 0.0180 +/- 0.0080 0.0180 +/- 0.0060 0.0150 +/- 0.0060 0.0140 +/- 0.0060 0.0150 +/- 0.0060 1110/2005 1/17/2005

- I 0.0172 +/- 0.0013 0.0204 +/- 0.0013 0.0156 +I- 0.0017 0.0141 +/- 0.0012 0.0149 +/. 0.0011 0.0139 +/- 0.0011 0.0128 +/- 0.0010 1/17/2005 1/24/2005 0.0205

+/-

0.0014 0.0238 +/- 0.0013 0.0238 +I- 0.0019 0.0221 +/- 0.0014 0.0222 +/- 0.0013 .

0.0212 +/- 0.0012 0.0233 +I- 0.0013 1/24/2005 1/31/2005 0.0171 +/- 0.0013 0.0168 +/- 0.0012 0.0182 +/- 0.0018 0.0186 +/- 0.0013 0.0183 +/- 0.0012 0.0169 +/- 0.0012 0.0177 +/- 0.0011 1/31/2005 2/7/2005 0.0264 +/- 0.0015 0.0254 +/- 0.0014 0.0255 +/- 0.0020 0.0259 +/- 0.0015 0.0240 +/- 0.0013 0.0220 +/- 0.0013 0.0276 +/- 0.0014 2/7/2005 2/14/2005 0.0207 +/- 0.0014 0.0219 +/- 0.0013 0.0217 +/- 0.0019 0.0222 +/- 0.0014 0.0216 +/- 0.0013 0.0201 +/- 0.0013 0.0229 +/- 0.0013 2114/2005 2/22005 0.0166 +/- 0.0012 0.0165

+/-

0.0011

. _ . . 0.0170 +/- 0.0016 0.0178 +/- 0.0012 0.0169 +/I 0.0011 0.0166 +/- 0.0011 0.0171 +/- 0.0011 2/22/2005 2/28t2005 0.0183 +/- 0.0014 0.0172 +/- 0.0013 0.0210 +I- 0.0020 0.0183 +/- 0.0014 0.0182 +/- 0.0013 0.0178 +/- 0.0013 0.0187 +/- 0.0013 2/28/2005 3/7/2005 0.0170 +/- 0.0013 0.0177 +/- 0.0012 0.0178 +/- 0.0018 0.0168 +/- 0.0013 0.0168 +/- 0.0012 0.0157 +/- 0.0011 0.0174 +/- 0.0012 3/7/2005 3/14/2005 0.0182 +/- 0.0013 0.0185 +/- 0.0012 0.0207 +/- 0.0018 0.0190 +/- 0.0013 0.0192 +/- 0.0012 0.0185 +/- 0.0012 0.0184 +/- 0.0012 3/14/2005 3/21/2005 0.0156 +/- 0.0012 0.0167 +/- 0.0012 0.0165 +/- 0.0017 0.0162 +/- 0.0013 0.0166 +/- 0.0011 0.0173 +/- 0.0012 0.0158 +/- 0.0011 3/21/2005 3/28/2005 0.0123 +/- 0.0011 0.0130 +/- 0.0011 0.0127 +/- 0.0015 0.0127 +4- 0.0012 0.0136 +/- 0.0011 0.0128 +/- 0.0010 0.0145 +/- 0.0011 3/28/2005 4/4/2005 0.0082 +/- 0.0010 0.0089 4/- 0.0010 0.0089 +/- 0.0015 0.0106 +/- 0.0011 0.0099 +/- 0.0010 0.0081 +/- 0.0009 0.0087 +/- 0.0009 4/4/2005 4111/2005 0.0143 +/- 0.0012 0.0137 +4- 0.0011 0.0148 +/- 0.0016 0.0156 +/- 0.0013 0.0141 +/- 0.0011 0.0139 +/- 0.0011 0.0156 +/- 0.0011 4/11/2005 4/182005 0.0174 +I- 0.0013 0.0186 +/- 0.0013 0.0190 +/- 0.0018 0.0205 +/- 0.0014 0.0189 +/- 0.0012 0.0175 +/- 0.0012 0.0193 +/- 0.0012 4/18/2005 4/25/2005 0.0126 +/- 0.0011 0.0131 +/- 0.0011 0.0144 +/- 0.0016 0.0144 +/- 0.0013 0.0138 +/- 0.0011 0.0139 +/- 0.0011 0.0117 +/- 0.0010 4/25/2005 -

5/2/2005 0.0101 +/- 0.0011 0.0123 +/- 0.0011 0.0107 +/- 0.0015 0.0116 +I- 0.0011 0.0116 +/- 0.0010 0.0109 +/- 0.0010 0.0121 +/- 0.0010 5/2/2005 5/9/2005 0.0143 +/- 0.0012 0.0144 +/- 0.0012 0.0133 +/- 0.0016 0.0146 +/- 0.0013 0.0135 +/- 0.0011 0.0141 +/- 0.0011 0.0133 +/- 0.0010 5/9/2005 5/16/2005 0.0134 +/- 0.0012 0.0151 +/- 0.0012 0.0151 +I- 0.0016 0.0147 +/- 0.0011 0.0153 +/- 0.0011 0.0152 +/- 0.0011 0.0149 +/- 0.0013 5/16/2005 5/23/2005 0.0087 +/- 0.0010 0.0098 +/- 0.0010 0.0079 +/- 0.0014 0.0090 +/- 0.0010 0.0092 +/- 0.009 0.0092 +/- 0.0010 0.0093 4/- 0.0010 5/23/2005 -

5/31/2005 0.0108 +/- 0;0010 0.0106 +I- 0.0010 0.0107 +/- 0.0013 0.0113 +/- 0.0009 0.0109 +/- 0.0009 0.0100 +/- 0.0009 0.0116 +/- 0.0009 5/31/2005 6/6/2005 0.0140 +/- 0.0013 0.0154 +/- 0.0013 0.0162 +/- 0.0018 0.0151 +/- 0.0012 0.0145 +/- 0.0012 0.0149 +/- 0.0012 0.0147 +/- 0.0013 6/6/2005 -

6/13/2005 0.0193 +/- 0.0013 0.0228 +/- 0.0014 0.0225 +/- 0.0018 0.0222 +/- 0.0014 0.0209 +/- 0.0013 0.0207 +/- 0.0013 0.0215 +/- 0.0023 6/13/2005 6/20/2005 0.0078 +/- 0.0010 0.0086 + 0.0010 0.0089 +/- 0.0012 0.0085 +/- 0.0009 0.0086 +/- 0.0009 0.0083 +/- 0.0009 0.0076 +/- 0.0017 6/20/2005 6/27/2005 0.0177 +/- 0.0013 0.0189 + 0.0013

-9 0.0187 +/- 0.0016 0.0196 +/- 0.0013 0.0178 +/- 0.0012 0.0191 +/- 0.0013 0.0187 +/- 0.0021 1st 6-Month Summary Maximum 0.0264 +/- 0.0080 0.0270 +/- 0.0080 0.0255 +/- 0.0100 0.0259 +/- 0.0060 0.0260 +/- 0.0060 0.0220 +/- 0.0060 0.0276 +/- 0.0060 Average 0.0156 0.0166 0.0166 0.0167 0.0162 0.0156 0.0164 Minimum 0.0078 +/- 0.0010 0.0086 +/- 0.0010 0.0079 +/- 0.0012 0.0085 +/- 0.0009 0.0086 +/- 0.0009 0.0081 +/- 0.0009 0.0076 +/- 0.0009 27

January 1 - December 31, 2005 Docket No. 50-244 I

Table B-Sb Concentration of Beta Emitters In Air Particulates-Onsite Samples Results in pCVM 3 + 2sigma Uncertainty START STOP Station #2 (l) Station #3 () Station #4 (I) Station #5 (I) Station #6 (I) Station #7 (I) Station #13 (1)

DATE DATE Manor House Yard East Field Training Center Creek Bridge Main Parking Lot West Fence Line Substation 13 Parking Lot 6/2712005 7/5/2005 0.0198 +/- 0.0012 0.0245 +1- 0.0013 0.0228 +/- 0.0018 0.0240 +/- 0.0013 0.0214 +/- 0.0012 0.0228 4/- 0.0012 0.0242 +/- 0.0021 7/5/2005 7/11/2005 0.0165 +/- 0.0014 0.0180 +4- 0.0014 0.01834+- 0.0017 0.0197 +/- 0.0014 0.0182 +/- 0.0013 0.0193 +/- 0.0014 0.0188 +/- 0.0023 7/11/2005 7/18/2005 0.0285 +/- 0.0015 0.0287 +/- 0.0018 0.0298 +/- 0.0019 0.0287 +/- 0.0015 0.0339 +/- 0.0022 0.0283 +/- 0.0015 0.0287 +/- 0.0024 7/18/2005 7/25/2005 0.0175 +/- 0.0013 0.0199 +/- 0.0014 0.0200 +/- 0.0017 0.0215 +/- 0.0013 0.0196 +/- 0.0019 0.0194 +/- 0.0016 0.0211 +/- 0.0022 7/25/2005 8/1/2005 0.0160 +/- 0.0012 0.0180 +/- 0.0012 0.0184 +/- 0.0016 0.0174 +/- 0.0012 0.0181 +/- 0.0018 I 0.0161 +/- 0.0013 0.0151 +/- 0.0020 8/1/2005 8/8/2005 0.0320 +'- 0.0016 0.0344 +/- 0.0017 0.0369 41. 0.0020 0.0355 +I/ 0.0016 0.0372 +1- 0.0023 0.0370 +/- 0.0018 0.0349 +/- 0.0026 8/8/2005 8/15/2005 0.0265 +/- 0.0015 0.0268 +/- 0.0014 0.0303 4/ 0.0019 0.0312 +/- 0.0016 0.0307 +/- 0.0021 0.0315 +/- 0.0017 0.0311 +/- 0.0024 I 8/15/2005 8/22/2005 0.0175 +/- 0.0013 0.0170 +/- 0.0011 0.0214 +/- 0.0017 0.0181 +/- 0.0012 0.0210 +/- 0.0018 0.0200 +/- 0.0014 0.0197 +/- 0.0021 8/22/2005 8/29/2005 0.0153 +/- 0.0012 0.0139 +/- 0.0010 0.0163 +/- 0.0015 0.0166 +/- 0.0012 0.0173 +/- 0.0017 0.0156 +/- 0.0012 0.0169 +/- 0.0020 8/29/2005 9/8/2005 0.0167 +1- 0.0011 0.0175 +/. 0.0010 0.0203 +/- 0.0015 0.0194 +/. 0.0012 0.0190 +/- 0.0016 0.0193 41- 0.0012 0.0196 +/- 0.0019

. _. _ . ,. _. _ . I 9/6/2005 9/12/2005 0.0238 +/- 0.0015 0.0228 +/- 0.0013 0.0265 4/- 0.0019 0.0250 +/- 0.0015 0.0251 +/- 0.0021 0.0256 +/- 0.0016 0.0267 +/- 0.0025 9/12/2005 9/19/2005 0.0305 +/- 0.0016 0.0311 +/- 0.0014 0.03286/- 0.0019 0.0332 +/- 0.0016 0.0334 +/- 0.0022 0.0358 +/- 0.0017

- 0.0302 +/- 0.0024 9/19/2005 9126/2005 0.0256 +/- 0.0015 0.0255 +/- 0.0013 0.0278 +/- 0.0018 0.0275 +/- 0.0014 0.0285 +/- 0.0020 0.0295 +/- 0.0016 0.0266 +/- 0.0023 9/26/2005 10/3/2005 0.0201 +/- 0.0013 0.0197 +I- 0.0012 0.0231 +1- 0.0017 0.0230 +/- 0.0013 0.0206 +/- 0.0018 0.0229 41- 0.0014 0.0199 +/. 0.0022 10/3/2005 10/10/2005 0.0195 +/- 0.0013 0.0193 4/- 0.0012 0.0201 +/- 0.0016 0.0188 +/- 0.0012 0.0223 +/- 0.0019 0.0212 +/- 0.0014 0.0192 +/- 0.0021 10/10/2005 10/17/2005 0.0055 +/. 0.0009 0.0046 +1- 0.0008 0.0047 +/. 0.0011 0.0054 +/- 0.0009 0.0048 +/- 0.0013 0.0046 +/- 0.0009

- 0.0033 4/- 0.0015 10/17/2005 10/24/2005 0.0124 +/- 0.0011 0.0112 +/- 0.0010 0.0121 +/- 0.0013 0.0124 +/- 0.0010 0.0142 +/- 0.0016 0.0128 +/- 0.0011 0.0119 +/- 0.0018 10/24/2005 10/31/2005 0.0113 +/- 0.0011 0.0119 +I 0.0010 0.0119 +1. 0.0013 0.0121 +I- 0.0010 0.0128 41. 0.0015 0.0131 41- 0.0011 -0.0111 4 0.0017 10/31/2005 11/7/2005 0.0288 +/- 0.0018 0.0299 4/- 0.0014 0.0310 +/- 0.0019 0.0326 +/- 0.0015 0.0310 +/- 0.0021 0.0351 +/- 0.0017 0.0279 4/- 0.0023 11/7/2005 11/14/2005 0.0184 +/- 0.0013 0.0191 4I- 0.0012 0.0202 +/- 0.0016 0.0196 +/- 0.0013 0.0178 +/- 0.0017 0.0194 +/- 0.0014

_ . _ . _ _ . _ . _ _ . _ 0.0200 +/- 0.0021 11/14/2005 11/21/2005 0.0175 +/- 0.0013 0.0178 +I- 0.0011 0.0187 +1 0.0015 0.0200 +/- 0.0012 0.0193 +/- 0.0017 0.0201 +/- 0.0013 0.0191 +/- 0.0020 11/21/2005 11128/2005 0.0138 +1- 0.0012 0.0137 +4- 0.0011 0.0152 +/- 0.0015 0.0149 +1- 0.0010 0.0131 +1- 0.0016 0.0137 +1- 0.0012

- 0.0122 +/- 0.0018 11128/2005 12/5/2005 0.0133 +I- 0.0012 0.0134 +/- 0.0010 0.0124 +/ 0.0014 0.0142 +/- 0.0012 0.0143 +/- 0.0016 0.0148 +/- 0.0012 0.0152 4/- 0.0019 12/5/2005 1211212005 0.0229 +/- 0.0014 0.0237 +/- 0.0013 0.0217 4/- 0.0016 0.0199 +/- 0.0012 0.0197 +/- 0.0017 0.0240 +/- 0.0014 0.0221 +/- 0.0021 12/12/2005 12/19/2005 0.0157 +I- 0.0012 0.0153 +/- 0.0011 0.0168 4/- 0.0015 0.0150 +/- 0.0011 0.0167 +/- 0.0017 0.0157 +/- 0.0012 0.0172 4/- 0.0020 12/1912005 12/26/2005 0.0338 +/- 0.0016 0.0368 +1- 0.0016 0.0344 +1 0.0018 0.0349 +/- 0.0015 0.0352 +/- 0.0020 0.0397 +/- 0.0017 0.0321 +/- 0.0022 12126/2005 1/3/2008 0.0143 4/- 0.0012 0.01658 /- 0.0011 0.01574/ 0.0015 0.0161 +/- 0.0011 0.0155 +/- 0.0016 0.0157 +/- 0.0012 0.0168 +/- 0.0019 2nd 6-Month Summaty Maximum 0.0338 +/- 0.0016 0.0368 +/- 0.0017 0.0369 +/- 0.0020 0.0355 +/- 0.0016 0.0372 +/- 0.0023 0.0397 +/- 0.0018 0.0349 +/-0.0026 Average 0.0197 0.0203 0.0215 0.0214 0.0215 0.0220 0.0208 Minimum 0.0055 +/- 0.0009 0.0046 +/- 0.0008 0.0047 +/- 0.0011 0.0054 +/- 0.0009 0.0048 +/- 0.0012 0.0046 +/- 0.0009 0.0033 +/-0.0015 12-Month Summary Maximum 0.0338 +/- 0.0080 0.0368 +/- 0.0080 0.0369 +/- 0.0100 0.0355 +/- 0.0060 0.0372 +/- 0.0060 0.0397 +/- 0.0060 0.0349 +/-0.0060 Average 0.0177 0.0185 0.0191 0.0191 0.0189 0.0188 0.0186 Minimum 0.0055 +/- 0.0009 0.0046 +/- 0.0008 0.0047 +/- 0.0011 0.0054 +/- 0.0009 0.0048 +/- 0.0009 0.0046 +/- 0.0009 0.0033 +/-0.0009 28

January 1 - December 31, 2005 Docket No. 50-244 Table B-6a Concentration of Beta Emitters in Air Particulates - Offsite Samples (Results in pCi/M3 + 2a Uncertainty)

START DATE STOP DATE Station #8 ( C ) Station #9 (I) Station #10 ( C ) Station #11 (I) Station #12 ( C )

Seabreeze Webster Walworth Williamson Sodus Point 12/27/2004 1/3/2005 0.0230 +1- 0.0080 0.0210 +/- 0.0100 0.0210 +/- 0.0080 0.0210 +/- 0.0080 0.0270 +/- 0.0080 1/3/2005 1/10/2005 0.0130 4/1 0.0060 0.0110 +/- 0.0080 0.0120 +/- 0.0060 0.0130 +/- 0.0060 0.0160 +/- 0.0060 1/17/2005 -----

1/10/2005 0.0185 0.0014 0.0206 +/- 0.0021 0.0228 +/- 0.0016 0.0160 4/ 0.0015 0.0152 +/- 0.0013 1/17/2005 1/24/2005 0.0242 0.0015 0.0215 +/- 0.0021 0.0227 +/- 0.0014 0.0229 4/ 0.0015 0.0241 +/- -0.0013 1/24/2005 1/31/2005 0.0173 4/-/- 0.0014 0.0164 +/- 0.0020 0.0149 +/- 0.0013 0.0173 +/- 0.0016 0.0175 +/- 0.0014 1/31/2005 27/2005 0.0266 0.0016 0.0237 +/- 0.0022 0.0264 +/- 0.0016 0.0237 4/ 0.0017 0.0251 +/- 0.0015 4/.. -

2/7/2005 2/14/2005 0.0226 /- 0.0015 0.0190 +/- 0.0021 0.0210 + 0.0015 0.0213 +/- 0.0016 0.0196 +/- 0.0013 2/14/2005 2/22(2005 0.0175 +/- 0.0013 0.0133 +/- 0.0016 0.0166 +/- 0.0012 0.0168 4/ 0.0013 0.0181 +/- 0.0012 2/22/2005 2/28/2005 0.0193 +1- 0.0015 0.0168 +/- 0.0021 0.0175 +/- 0.0014 0.0173 +/- 0.0016 0.0158 +/- 0.0013 2/28/2005 3/7/2005 0.0164 /- 0.0013 0.0169 +/- 0.0020 0.0156 +/- 0.0013 0.0166 +/ 0.0015 0.0164 +/- 0.0012 3/7/2005 3/14/2005 0.0179 0.0014 0.0160 4/. 0.0019 0.0170 +/- 0.0013 0.0174 4/ 0.0015 0.0191 +/- 0.0013 3/14/2005 3/21/2005 0.0184 0.0014 0.0155 +/- 0.0019 0.0166 +/- 0.0013 0.0153 +/- 0.0014 0.0144 +/- 0.0012 3/21/2005 3/28/2005 0.0143 0.0013 0.0111 +/- 0.0017 0.0130 +/- 0.0012 0.0129 4/ 0.0013 0.0120 +/- 0.0011 3/28/2005 4/4/2005 0.0107 +J- 0.0012 0.0095 +/- 0.0017 0.0103 +/- 0.0012 0.0097 4/ 0.0013 0.0101 +/- 0.0011 4/4/2005 4/11/2005 0.0157 4- 0.0013 0.0124 4/. 0.0017 0.0158 +/- 0.0013 0.0147 /. 0.0014 0.0141 +/- 0.0012 4/11/2005 4/18f2005 0.0197 0.0015 0.0194 +/- 0.0021 0.0189 +/- 0.0014 0.0182 4/ 0.0015 0.0171 +/- 0.0013 4/18/2005 4/25/2005 0.0153 4- 0.0013 0.0131 +J- 0.0018 0.0135 +/- 0.0013 0.0144 4/ 0.0014 0.0117 +/- 0.0011 4/25/2005 5/2/2005 0.0129 4-4/- 0.0013 0.0107 4/- 0.0017 0.0120 +/- 0.0012 0.0118 ./ 0.0013 0.0107 +/- 0.0011

+1. - -

5/212005 5/9/2005 0.0162 0.0014 0.0125 +/- 0.0017 0.0145 +/- 0.0013 0.0134 4/ 0.0014 0.0129 +/- 0.0011

+1-5/9/2005 5/16/2005 0.0185 4- -

0.W015 0.0153 +/- 0.0012 0.0155 +/- 0.0013 0.0142 4/- 0.0012 0.0143 +/- 0.0013 5/16/2005 5/23/2005 0.0116 0.0012 0.0093 +/- 0.0010 0.0101 +/- 0.0012 0.0091 4/. 0.0010 0.0092 +/- 0.0010 5/23/2005 5/31/2005 0.0137 4- -

0.0012 0.0103 4 0.0009 0.0111 +/- 0.0011 0.0109 +/- 0.0010 0.0098 +/- 0.0010 5/31/2005 6/6/2005 0.0174 0.0016 0.0137 4/ 0.0012 0.0158+/ 0.0015 0.0146 +1 0.0013 0.0128 +/- 0.0012 6/6/2005 6/13/2005 - -

0.0240 4- -

0.0016 0.0216 +/- 0.0013 0.0211 +/- 0.0015 -

0.0223 4/ 0.0014 0.0195 +/- 0.0013 6/13/2005 6/20/2005 0.0098 /- 0.0012 0.0076 4/ 0.0009 0.0084 +/- 0.0011 0.0073 +/- 0.0010 0.0077 +/- 0.0010 6/20/2005 6/27/2005 0.0225 0.0016 0.0188 4. 0.0013 0.0212 - 0.0015 0.0203 4/ 0.0014 0.0193 +/- 0.0013 1st 6-Month Summary Maximum 0.0266 +/- 0.0080 0.0237 +/- 0.0100 0.0264 +/- 0.0080 0.0237 +/- 0.0080 0.0270 +/- 0.0080 Average 0.0176 0.0153 0.0164 0.0159 0.0158 Minimum 0.0098 +/- 0.0012 0.0076 +/- 0.0009 0.0084 +/- 0.0011 0.0073 +/- 0.0010 0.0077 +/- 0.0010

January 1 - December 31, 2005 Docket No. 50-244 Table B-6b Concentration of Beta Emitters In Air Particulates-Offsite Samples Results in pCimM3 + 2sigma Uncertainty START DATE STOP DATE Station #8 (C) Station #9 (l) Station #10 ( C ) Station #11 () Station #12 ( C )

Seabreeze Webster Walworth Williamson Sodus Point 6/27/2005 7/512005 0.0286 +/- 0.0016 0.0235 41- 0.0013 0.0246 +/- 0.0015 0.0232 0.0013 0.0221 0.0013 7/5/2005 -

7/11/2005 0.0215 +/- 0.0017 0.0177 4/- 0.0014 0.0188 +/- 0.0016 0.0173 0.0014 0.0180 0.00114 7/11/2005 7/18/2005 0.0329 +/- 0.0018 0.0280 4/- 0.0015 0.0272 +/- 0.0015 0.0017 0.0260 0.0015 0.0254 7/-

7118/2005 7/25/2005 0.0235 4/- 0.0016 0.0184 +1- 0.0013 0.0197 +/- 0.0015 0.0184 0.0014 0.0184 +1- 0.0013 4'. 4/- -

7/25/2006 8/11/2005 0.0183 +/- 0.0015 0.0159 0.0012 0.0167 +/- 0.0014 0.0152 0.0013 0.0154 0.0012 8/1/2005 8/8/2005 0.0397 0- 0.0020 0.0344 4/- 0.0016 0.0326 +/- 0.0018 0.0325 4/- 0.0017 0.0344 0.0017 8/8/2005 8/15/2005 4/-

+1-0.0263 +1- 0.0015 0.0274 0.0015 0.0013 0.0276 0.0015 0.0251 +/- +1- 0.0016 0.0282 8/15/2005 -

8/22/2005 0.0168 +I- 0.0013 0.0180 4/-

0.0012 0.0179

+/- 0.0012 0.0189 0.0014 0.0183 4/- 0.0013 8/22/2005 8/29/2005 0.0153 +/- 0.0012 0.0134 0.0011 0.0158 +/- 0.0011 0.0169 4/- 0.0013 0.0163 0.0012 8/29/2005 9/6/2005 0.0011 4/- 0.0012 0.0179 +1 0.0012 0.0180 0.0166 4/- 0.0010 0.0184 0.0012 0.0170 9/6/2005 9/12/2005 0.0248 +/- 0.0016 0.0258 0.0015 0.0252 +/- 0.0014 0.0258 +1- 0.0017 0.0268 4/- 0.0016 9/12/2005 9/19/2005 0.0329 +/- 0.0017 0.0299 0.0015 0.0303 +/- 0.0014 0.0304 0.0016 0.0313 0.0016 9/19/2005 4/- 0.0015 +1- -

9/26/2005 0.0270 +/- 0.0015 0.0290 0.0264 +/- 0.0014 0.0246 0.0015 0.0279 0 .00 15 9/26/2005 10/3/2005 0.0221 +/- 0.0014 0.0204 +1- 0.0013 0.0196 +/- 0.0012 0.0205 4/-

0.0014 0.0194 0.0013 10/3/2005 10/10/2005 0.0199 +.- 0.0014 0.0183 0.0013 0.0191 +/- 0.0012 0.0195 0.0014 0.0080 0.0015 10/10/2005 10/17/2005 0.0050 4/- 0.0009 4/-

0.0008 +1- 0.0008 0.0048 0.0044 +/- 0.0008 0.0044 0.0009 0.0045 10/17/2005 10/24/2005 0.0120 4/- 0.00 11 0.0131 +1- 0.0011 0.0113 +/- 0.0010 0.0116 +1- 0.0011 0.0105 0.0010 10/24/2005 10/31/2005 0.0132 +/- 0.0012 0.0122 0.0010 0.0121 +1- 0.0010 0.0122 0.0011 0.0118 0.0010

+1-10/31/2005 11/7/2005 0.0308 +/- 0.0016 0.0295 0.0015 0.0279 +/- 0.0014 0.0294 0.0016 0.0289 0.0015 11/7/2005 11/14/2005 0.0209 4/- 0.0014 0.0190 0.0013 0.0185 +/- 0.0012 0.0188 0.0013 0.0182 0.0013 11/14/2005 11/21/2005 0.0193 +/- 0.0013 0.0180 0.0012 0.0196 +/- 0.0012 __

0.0196 0.0013 0.0189 0.0012 11/21/2005 +1- 0.0011 0.0011 0.0012 11/28/2005 0.0117 +/- 0.0012 0.0121 0.0131 +/- 0.0111 0.0011 0.0139 11/28/2005 12/5/2005 0.0092 +/- 0.0015 0.0126 0.0010 0.0134 +/- 0.0011 0.0126 0.0011 0.0141 0.00 11 12/5/2005 12/12/2005 0.0183 +/- 0.0013 0.0224 0.0013 0.0218 +/- 0.0013 0.0180 0.0013 0.0230 0.0013 12/12/2005 12/19/2005 0.0137 +/- 0.0012 0.0151 0.0011 0.0155 +/- 0.0011 0.0154 0.0012 0.0164 0.0012 12/19/2005 12/26/2005 0.0380 +I/- 0.0017 0.0214 0.0012 0.0358 +/. 0.0015 0.0338 0.0016 0.0310 0.0014 12/26/2005 1/3/2006 0.0181 +/- 0.0013 0 .0 114 0.0010 0.0148 +1- 0.0011 0.0148 -

0.0012 0.0140 -

0.0011 2nd 6-Month Summary Maximum 0.0397 +/- 0.0020 0.0344 +/- 0.0016 0.0358 +/- 0.0018 0.0338 +/- 0.0017 0.0344 +/- 0.0017 Average 0.0213 0.0196 0.0201 0.0199 0.0197 Minimum 0.0050 +/- 0.0009 0.0048 +/- 0.0008 0.0044 +/- 0.0008 0.0044 +/- 0.0009 0.0045 +/- 0.0008 12-Month Summary Maximum 0.0397 +/- 0.0080 0.0344 +/- 0.0100 0.0358 +/- 0.0080 0.0338 +/- 0.0080 0.0344 +/- 0.0080 Average 0.0195 0.0175 0.0183 0.0179 0.0178 Minimum 0.0050 +/- 0.0009 0.0048 +/- 0.0008 0.0044 +/- 0.0008 0.0044 +/- 0.0009 0.0045 +/- 0.0008

January 1 - December 31, 2005 Docket No. 50-244 Table B-7 Concentration of Gamma Emitters in Air Particulates (Results in units of 10-2 pCi/m 3 +/- 2a)

Location 'irst Second ' Third' Four Quarter Quarter Quarter Quarter Station #2 * * * *

,:Monornus&Yard.  ::  :- ,--  :  ; -

~$ai n# . _ *

  • East Field Station #4. * * *
  • rStabo 00< / * *- -*

> i (

0 --* v6tidi Creek Bridge F-- 77 Station #6 * * *

  • ain Fark ng ot C Sa'ti'oir#7
  • 0* ;v ~*_-raR*vd-aesS w s 9o D West Fence Line Station #8 * *
  • iSeabreeze-. ' -  : '  : = '  :'  :' '-: °' ':":'

Webster Station #10 * *

  • Williamson Station #12 * ** *

~Station #13 Substation 13

  • All Non-Natural Gamma Emitters <MDA 31

January 1 - December 31, 2005 Docket No. 50-244 Table B-8 Concentration of Gamma Emitters inVegetation Samples (Results in units of pCi/kg (wet) + 2a) 1;4,,,z.-~

1 ... . , . E L6cati on

ampe ;- 3I Samrnple ' ' ' Gam'ma Date Type Emitters FIr'-  : -w ve_.p ....

SE Garden 07/20/2005 Lettuce

  • 08 61/005 Tomatoes -

ESE Garden 07/26/2005 Lettuce

  • 08/08/2605 mtot es ,

Control Garden 07/26/2005 Lettuce *

- , 7 08/082005 .- Tomatos 09/15/2005 Apples *

- 091i5/2n05 - aCbge

  • Site Code f 09 01205 . ab.!ge Site Code 31-SSE 09/15/2005 Apples
  • slte Code i-  ; -'ii' 09/1 /2005 Apples
  • Site Code 31-WSW 09/15/2005 Apples *
  • All Non-Natural Gamma Emitters <MDA 32

January 1 - December 31, 2005 Docket No. 50-244 Table B-9 Concentration of Gamma Emitters (including 1-131) in Milk (Results in units of pCi/Liter +/- 2O)

!Location Sample OGa'mma Date Emitters FARM A 02/8/2005

  • 77-S. - t- tion 71 7 04i11-210 - *0-0-6 06/14/2005 *

' ' 06/28/200 07/12/2005 *

-7/25/2005 -

  • 08/08/2005
  • 09/08/2005
  • 09/20/2005 *.....

10/04/2005

  • 11/07/2005 3/2005 12/1xesrvs Xr. -t*

AM8  ? ' 1711/2005 C

station 22 03/08/2005 *

.. 7*- 5f1/2005 06/14/2005

  • 28/20 5 06 /-7--

07/12/2005

  • 7 7. .- .?I2[

08/09/2005 *

[77'7 ' 0813/203i05-09/07/2005 -

10/04/2005

  • F7`

Station 24 02/08/2005

  • _rr, T3077205.-7---

04/11/2005 r7srr-f7T7 06/14/2005

  • w90622OU-.

07/12/2005

  • 0 ?57/2 05 w*

33

January 1 - December 31, 2005 Docket No. 50-244 Table B-9 (Continued)

Concentration of Gamma Emitters (including 1-131) in Milk (Results in units of pCVLiter +/- 2a)

Location .  : -: I -Sample S -X Gamma Date Emitters FARM D (Continued) 09/08/2005 *

-O9/2 1200- -,*,

10/04/2005*

11/07/2005 *

  • Ail Gamma Emitters, including 1-131, <MDA 34

January 1 - December 31, 2005 Docket No. 50-244 Table B-I 0 Typical MDA Ranges for Gamma Spectrometry Selected Water Fish Sediment Particulate Vegetation Milk

. N cli es-p--"__-I -Ci ICIg ~16'-iK

.i...-/I--,-,1'j O /mpC ri :~ Ci/k

-~ 4-3 '723 Z779 -

Na-22 4 -10 27 -51 47 -160 0.4 -1.0 21 -68 6 -13 7'rZ51 128-77 272'777 3 3-i380 142-277 14_3-3 80 1-_61 Mn-54 4 -8 20-39 39 -118 0.5 -0.9 15 -56 5 -10 Fe-59 8-11 69 -191 118-436 3 -6 45 -144 11 -24 F0 A' 24-7 49 144~O51. 21-70 51 Zn-65 8 -21 53 -95 102 -365 3 -3 45 -166 12 -25 Zr-95 6 -16 47 -94 75 -259 1-3 34 -102 8 -16 1f5-267,: 31 9 -2~ 4f~ ~4944O ~ -75 Ag-110m 3 -8 20 -31 37 -142 0.4 -0.8 16 -52 4- 8

[r-129nr '4WT9 ~364 ~12 f1 58-20 19-33 246 -674' 50-8, 1-131 4 -29** 100 -12200 122 -1300 161 -827* 21 -479 4-9*

'33-I17' . 14-51 - 4-8 Cs-137 4 -8 21 -32 39 -125 0.3 -0.7 18 -57 5-10 77 t 777 s9-22607 0- 93 7~7_~14 La-140 r 6 -29 59 -2250 777fo 103 -916 Tb7 7 33 -87 29 -137 19 6-14 20 J43 The MDA range for 1-131 measured in'drinking water istypically 0.5 to 1.1 pCiIL h~N-_an~' forl1-131 measuredinmilk Yis tyicalyip LL~~

35

January 1 - December 31, 2005 Docket No. 50-244 Table B-11 Typical LLDs for Gamma Spectrometry Selected Water Fish Sediment Particulate

  • Vegetation Milk

_ . ,:~ PC i - Ur PC  :

Cr-51 26 120 327 16 162 70

. 3. 0: g27 49 2.8 7`77; Co-58 3.9 20 36 2.8 25 RS- ,F-9 ,7.;--f- -';4 0 '- >% -6 Co-60 4.4 24 60 2.7 33 Nb-95 4.2 18 60 2.4 25 Ru-106 35 172 458 25 223 Te-129m 41 170 551 27 265 7<7>1---~; 3  ; "'-41' ' '-A -'0'.4':' '

Cs-134 3.3 17 44 2.4 24 6 7 3 3 17 58 - 27 6 Ba-140 4.8 19 67 3.9 80 7 Ce-144 17 58 191 8.9 101 S w.> .w ... .+, :, is ... .. - e . ... , , ,;

... >...:+:

+.:'.............;...v..

.X:.w;.i.

.,_<b+.'

v w....._.

  • The LLD for 1-131 measured on a charcoal cartridge is typically 0.013 - 0.054 pCi/M3 36

January 1 - December 31, 2005 Docket No. 50-244 Table B-12 Direct Radiation (Results in Units of mR/90 days +/- 2a)

Station Location First Quarter Second Quarter Third Quarter Fourth Quarter 2 Onsite-Manor House Yard 11.0 i 2.8 12.9 +/- 3.3 12.5 i 3.1 12.4 +/- 3.1 3 pt ' n "' ~ 4~ 7"'-"'1'2.7 '3'.2" t ' 1.1 +/- 3'2 12.'

1 +/- 3.0 SE of station #2 4 Onsite-Training Center yard 11.6 +/- 2.9 13.3 i 3.4 12.6 +/- 3.2 12.9 +/- 3.3 driveway circle enc71 a1r8tw 31 siFs1r -t '141er4 z t 173.67i 3A - 13.0 +/- 3.3 entry road 6 Onsite-SW side of plant parking lot 9.3 +/- 2.3 10.4+/- 2.6 9.8 +/- 2.5 9.8 +/- 2.5 7' ity o aW Tlnt ,-13.7 +/- 3.4'"t v 17.3; i-44 15. 58<

+/-i3.9 150- 3.85 fence 8' TopperDrive-lrondequoit, 10.1 +/-2.5 11.5 2.9 11.0+/-2.8 11.0+/-2.8 Seabreeze Substation #51 B-t 70n 9.6 2.4" 11.84+/- 0 11.2 ' .8 f 6 21.0'28' 0' '1 '77 with Highway #104, Substation #74 10 1 Atlantic Avenue-Walworth, 9.0 +/- 2.3 10.4 +/- 2.6 9.8 +/- 2.5 10.4 +/- 2.6 Substation #230

- 9.94 2.5 10.9 +/-2

. 7 9'II 10.3.. 2.8 i8 2.7 Substation #207 121 12 Seaman Avenue-Sodus Point-Off 10.2 2.6 11.5 2.9 11.3 2.9 11.4 2.9 Lake Road by Sewer district, Substation #209 ffTrea' ' 1.4 2.9 135 13.1.334 - 12.8+/- 3.2

  • -'fenceand dogleg to West 14 NW corner of field along lake shore 10.3 +/- 2.6 12.5 +/- 3.2 12.4 +/- 3.1 12.0 +/- 3.0

> rfadE~t ~f~T rchard, 11.5i2.9 13.6+/-3.4 13.1 3.3 ' 13.1 3.3' approximately 3000' West of plant 16 SW Comer of orchard, 10.7 2.7 12.8 3.2 12.5 3.2 12.1 +/-3.1 approximately 3000' West of plant, 37

January 1 - December 31, 2005 Docket No. 50-244 approximately 200' North of Lake Road z ~t17 Uilt pl in orcperd &2 ~ -ppoxma i2N~f' S -O~ waytr6fi4 r.9rsA 75" North of Lake Road 18 Approximately 30' North of NE 10.1 i2.5 12.2 3.1 11.2 2.8 11.2 2.8 comer of Substation 13A fence h9is of.4T2'4 A 0 27S 5 96 +/-2.4 plant access road 20 Approximately 150' West of Ontario 10.3 +/- 2.6 12.2 +/- 3.1 12.2 +/- 3.1 11.6 +/- 2.9 Center Road and approximately 170' South of Lake Road approximately 200' East of Ontario Center Road 22 North side of Lake Road, SE, 9.5 2.4 11.3 2.8 11.2 2.8 10,8 2.7 property owner

5 9.2.5 '- 12.0+3.0 ' 12.6 +/-2 3 0 : -~Lake Road' and Lake shore - >  :

24 Lake shore near NE comer of 10.6 +/- 2.7 12.7 +/- 3.2 12.8 +/- 3.2 12.9 i 3.2 property

' "25 ~ ' ' ~ -v':10'.7+/-2.7 "t"'i2:'0 1 3.0D'"'-'

+/- 10'.6 2'.7 D# 01-0.8 +/-2.7 adjacent to 897 Klem Road -

261 Service Center, Plank Road, West of 9.9 i 2.5 11.7 3.0 i 10.8 i 2.7 10.9 +/- 2.8 250 A7N...... t o' 9.8'++/-2.5 12733.1 11.9+/- 3.0 1O.&t 27 utility pole, North side of road 28 Substation #193, Marion, behind 9.5 i 2.4 10.9 +/- 2.7 10.6 +/- 3.7 11.1 +/- 2.8 Stanton Ag. Service, North Main Street__

ibF#2ob-t6-Wmntffi bad 9.4 ,4 ¢2.8' 1 1'0.1 +/-2.6 10.5i2-6 (CR- 18), 1000' North of Route 104 30 ' District Office, Sodus, on pole, West 10.4 i 2.6 10.7 i 2.7 11.1 +/- 2.8 10.5 i 2.7 side of bldg 31 10.8 2.7 12.9 3.2' 12.'8 i 3.2 '12.03.0 500'"East of Salt Road 32 Woodard Road at County Line 9.2 +/- 2.3 10.9 +/- 2.8 10.4 +/- 2.6 10.3 +/- 2.6 Road, pole @ BW corner 38

January 1 - December 31, 2005 wF?.

Docket No. 50-244 i, ^ :33 -County Line Roaa at RR tracKs, pate 11.2 4 2.5 10.7 +/- 2.7 10.6 +/- 2.7 approximately 100' East along tracks 34 Lincoln Road, pole midway between 10.3 +/- 2.6 12.8 +/- 3.2 12.5 +/- 3.1 11.8 +/- 3.0 Ridge Road and Route 104 aths to VMS -7 1 - .3 # 3.2 Clevenger Road on pole, 36 Substation #205, Route 104, East of 9.5 i 2.4 11.6 +/- 2.9 11.0 +/- 2.8 10.9 +/- 2.7 Ontario Center Road, North side of fence r- 31inf

-777 ia

-~

,t, .

9.d32 .

2.

0

-T.' 2.

i f

'%OT 0.

6& 10.1 0.

+/-2.5 38 Fisher Road at RR Tracks, pole East 10.4 +/- 2.6 12.3 +/- 3.1 12.5 +/- 3.1 11.6 +/- 2.9 of road West of intersection with Stony Lonesome Road 40 Lake Road at Stoney Lonesome 9.6 +/-2.4 11.0 +/-2.8 10.6 +/-2.7 10.2 +/-2.6 Road, pole at SE comer

-Co tro Location

'Control Location 39

January 1 - December 31, 2005 Docket No. 50-244 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 generally agree with the intercomparison laboratory results within +/-2 a of each other, and both sets of results are also in agreement when using the NRC Resolution Test Criteria' for evaluation. 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 .

All the results contained in Table C-2 generally agree with their respective Constellation Energy Laboratory replicates and/or split laboratory samples, except for three comparisons of soil samples involving Cs-137 results. The original analysis of the soil sample from SFS2 and the split analysis of the soil sample from SFS3, both of which were collected on 3/21/05, and the replicate analysis of the soil sample from SFS2 collected on 9/5/2005 do not agree within +/-2u of their respective QC soil samples analyzed. These minor discrepancies, which have been observed in previous reporting periods, are most probably due to counting statistics and/or the non-homogeneous nature of this type of sample. As indicated in Table C-2, there was an instance where activity was observed in split sample, but not observed in either the original or replicate samples (viz., the 3/21/05 vegetation sample from SFb2). 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 40

January 1 - December 31, 2005 Docket No. 50-244 TABLE OF CONTENTS - ANALYTICAL RESULTS Table Title Page C-1 Results of Participation in Cross Check Program .................................................... 42 C-2 Results of Quality Assurance Program .................................................... 45 C-3 Teledyne Brown Engineering's Typical MDAs for Gamma Spectrometry ............................. 53 41

TABLE C-1 Results of Participation in Cross Check Programs Sample Sample Type Isotope Reported Cross Check Date and Units Observed Laboratory's Lab Results' Results' 2/15/05 Water-pCUiL Ba-1 33 48+/-7 53+/-5 Co-60 61+/-7 57+/-5 Cs-134 62+/-6 65+/-5 Cs-1 37 45+/-9 40+/-5 Zn-65 178+/-24 161+/-16 3/17/05 Milk-pCiUL 1-131 111+/-14 92+/-3 Cs-134 145+/-11 139+/-5 Cs-137 156+/-16 130+/-4 Ce-141 285+/-19 229+/-8 Cr-51 420+/-95 334+/-11 Mn-54 181+/-S15 160+/-5 Co-58 127+/-S15 115+/-4 Fe-59 137+/-19 111+/-4 Co-60 164+/-12 144+/-5 Zn-65 229+/-32 198+/-7 3/17/05 Charcoal 1-131 73+/-7 60+/-2 Cartridge-pCi 3/17/05 Water-pCiUL Gross ,3 271 +/-2 268+/-9 5/17/05 Water-pCUL 1-131 15+/-1 16+/-3 6/6/05 Water-pCi Gross P 216+/-3 214+/-7 6/9/05 Water-pCUL Cs-134 90+/-19 104+/-3 Cs-137 217+/-33 206+/-7 Co-60 163+/-23 158+/-5 Mn-54 144+/-31 136+/-5 Zn-65 162+/-67 169+/-6 6/9/05 Filter-pCi/filter Beta 77+/-2 83+/-3 1See discussion at the beginning of the Appendix.

42

TABLE C Continued Results of Quality Assurance Program Sample Sample Type Isotope Reported Cross Check Date and Units Observed Laboratory's Lab Results' Results' 6/9/05 Filter-pCi/filter Ce-141 72+/-6 61+/-2 Cr-51 252+/-42 200+/-7 Cs-1 34 56+/-4 63+/-2 Cs-137 131+/-8 125+/-4 Mn-54 92+/-7 83+/-3 Fe-59 48+/-8 42+/-1 Zn-65 116+/-13 102+/-3 Co-60 103+/-6 96+/-3 8/16/05 Water-pCi/L Ba-1 33 104+/-10 106+/-11 Cs-134 82+/-6 92+/-5 Cs-137 77+/-9 73+/-5 Zn-65 61+/-14 66+/-7 Co-60 13+/-5 14+/-5 11/15/05 Water-pCUL 1-131 18+/-3 17+/-3 12/08/05 Water-pCi/L Gross ,3 245+/-3 285+/-10 12/08/05 Water-pCi/L 1-131 56+/-10 53+/-2 Ce-141 161+/-13 165+/-6 Cr-51 129+/-57 142+/-5 Cs-134 60+/-6 64+/-2 Cs-137 141+/-13 139+/-5 Co-58 61+/-9 57+/-2 Mn-54 116+/-11 112+/-4 Fe-59 62+/-12 61+/-32 Zn-65 122+/-20 113+/-4 Co-60 80+/-8 81+/-3 1 See discussion at the beginning of the Appendix 43

TABLE C Continued Results of Quality Assurance Program Sample Sample Type Isotope Reported Cross Check Date and Units Observed Laboratory's Lab Results' Results3 12/08/05 Milk-pCi/L 1-131 82+/-20 75+/-2 Ce-141 249+/-24 224+/-7 Cr-51 223+/-129 193+/-6 Cs-1 34 92+/-12 87+/-3 Cs-1 37 223+/-26 189+/-6 Co-58 84+/-17 78+/-2 Mn-54 187+/-23 152+/-5 Fe-59 63+/-25 82+/-3 Zn-65 182+/-40 154+/-5 Co-60 127+/-16 111+/-4 12/8/05 Filter-pCi/filter Ce-141 234+/-9 205+/-7 Cr-51 212+/-40 177+/-6 Cs-134 69+/-6 80+/-3 Cs-137 191+/-10 173+/-6 Co-58 75+/-7 71+/-2 Mn-54 159+/-9 139+/-5 Fe-59 86+/-9 75+/-2 Zn-65 164+/-16 141+/-5 Co-60 108+/-6 101+/-3 12/8/05 Charcoal 1-131 95+/-7 74+/-2 Cartridge-pCi 3 See discussion at the beginning of the Appendix 44

TABLE C-2 Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split And Location Date Analysis Analysis Analysis Analysis 102 pCi/M 3 Air lodine-A3 1/03/05 1-131 <1.4 <1.5 **

Air lodine-A4 1/03/05 1-131 <1.1 <1.3 **

Air Filter -Al 1/03/05 Beta 3.0+/-0.3 3.1+/-0.3 **

Air Filter -A2 1/03/05 Beta 2.5+/-0.2 2.8+/-0.2 **

Air Filter -A3 1/03/05 Beta 2.6+/-0.2 2.5+/-0.2 **

Air Filter -A4 1/03/05 Beta 2.9+/-0.2 2.9+/-0.2 **

Air Filter -A5 1/03/05 Beta 3.2+/-0.2 3.2+/-0.2 **

Air Filter -SFAI 1/03/05 Beta 2.8+/-0.2 2.7+/-0.2 **

Air Filter -SFA2 1/03/05 Beta 2.8+/-0.2 3.0+/-0.2 **

Air Filter -SFA3 1/03/05 Beta 3.2+/-0.2 3.2+/-0.2 **

Air Filter -SFA4 1/03/05 Beta 2.9+/-0.2 3.4+/-0.2 **

102 pCi/m3 Air Filter-Al 2/07/05 Beta 2.2+/-0.2 2.0+/-0.2 **

Air Filter-A2 2/07/05 Beta 1.7+/-0.3 1.8+/-0.3 **

Air Filter-A3 2/07/05 Beta 1.9+/-0.2 1.9+/-0.2 **

Air Filter-A4 2/07/05 Beta 2.1+/-0.2 2.0+/-0.2 **

Air Filter-A5 2/07/05 Beta 2.2+/-0.2 2.2+/-0.2 **

Air Filter-SFA1 2/07/05 Beta 1.9+/-0.2 2.0+/-0.2 **

Air Filter-SFA2 2/07/05 Beta 2.2+/-0.2 2.2+/-0.2 **

Air Filter-SFA3 2/07/05 Beta 2.3+/-0.2 2.1+/-0.2 **

Air Filter-SFA4 2/07/05 Beta 2.2+/-0.2 2.4+/-0.2 **

Air Iodine-Al 2/07/05 1-131 <1.2 <1.4 **

Air lodine-A2 2/07/05 1-131 <1.1 <1.3 **

pCi/L Bay Water-Wa2 2/25/05 Gamma <MDA <MDA <MDA

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

45

TABLE C Continued Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split And Location Date Analysis Analysis Analysis Analysis l0o, pCi/m 3 Air Filter-Al 3/07/05 Beta 1.3i0.2 1.4+/-0.2 **

Air Filter-A2 3/07/05 Beta 1.5+/-0.2 1.8+/-0.2 **

Air Filter-A3 3/07/05 Beta 1.6+/-0.2 1.6+/-0.2 **

Air Filter-A4 3/07/05 Beta 1.6+/-0.2 1.6+/-0.2 **

Air Filter-A5 3/07/05 Beta 1.5+/-0.2 1.7+/-0.2 **

Air Filter-SFAI 3/07/05 Beta 1.6+/-0.2 1.6+/-0.2 **

Air Filter-SFA2 3/07/05 Beta 1.5+/-0.2 1.8+/-0.2 **

Air Filter-SFA3 3/07/05 Beta 1.7+/-0.2 1.9+/-0.2 **

Air Filter-SFA4 3/07/05 Beta 1.8+/-0.2 1.8+/-0.2 **

Air Iodine-A3 3/07/05 1-131 <1.5 <1.6 **

Air lodine-A4 3/07/05 1-131 <1.3 <1.5 **

pCi/Kg Soil-SFS2 3/21/05 Cs-137 82+/-24 165+/-56 116+/-14 Soil-SFS3 3/21/05 Cs-137 581+/-115 531+/-92 379+/-22 Vegetation-SFb2 3/21/05 Cs-137 <MDA <MDA 20+/-10 Vegetation-SFb3 3/21/05 Cs-I 37 <MDA <MDA <MDA Oysters-la3 3/30/05 Gamma <MDA <MDA <MDA pCi/L Bay Water-Wa2 3/31/05 Gamma <MDA <MDA <MDA

,10pCi/m 3 Air Filter-Al 4/04/05 Beta 0.6+/-0.2 0.6+/-0.2 **

Air Filter-A2 4/04/05 Beta 0.6+/-0.2 0.6+/-0.2 **

Air Filter-A3 4/04/05 Beta 0.5+/-0.2 0.5+/-0.2 **

Air Filter-A4 4/04/05 Beta 1.0+/-0.2 0.8+/-0.2 **

Air Filter-A5 4/04/05 Beta 0.8+/-0.1 0.8+/-0.1 **

Air Filter-SFAI 4/04/05 Beta 0.7+/-0.2 0.7+/-0.2 **

Air Filter-SFA2 4/04/05 Beta 0.6+/-0.2 0.6+/-0.2 **

Air Filter-SFA3 4/04/05 Beta 0.7+/-0.2 1.0+/-0.2 **

Air Filter-SFA4 4/04/05 Beta 0.7+/-0.2 1.0+/-0.2 **

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

46

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 Iodine-Al 4/04/05 1-131 <1.5 <1.5 **

Air Iodine-A2 4/04/05 1-131 <1.4 <1.3 **

10.2 pCi/M3 Air lodine-A3 5/16/05 1-131 <1.5 <1.3 **

Air lodine-A4 5/16/05 1-131 <1.5 <1.5 **

Air Filter-Al 5/16/05 Beta 0.9+/-0.2 1.1+/-0.2 **

Air Filter-A2 5/16/05 Beta 0.8+/-0.2 0.8+/-0.2 **

Air Filter-A3 5/16/05 Beta 0.9+/-0.1 0.7+/-0.2 **

Air Filter-A4 5/16/05 Beta 1.1+/-0.2 1.2+/-0.2 **

Air Filter-A5 5/16/05 Beta 1.1+/-0.2 1.1+/-0.1 **

Air Filter-SFAI 5/16/05 Beta 0.8+/-0.2 0.9+/-0.1 **

Air Filter-SFA2 5/16/05 Beta 0.9+/-0.2 1.0+/-0.2 **

Air Filter-SFA3 5/16/05 Beta 1.2+/-0.2 1.3+/-0.2 **

Air Filter-SFA4 5/16/05 Beta 0.9+/-0.2 1.0+/-0.2 **

pCi/Kg Shoreline-Wbl 5/09/05 Gamma <MDA <MDA <MDA

-,1 pCi/m 3 Air Filter-Al 6/6/05 Beta 0.8+/-0.2 1.0+/-0.2 **

Air Filter-A2 6/6/05 Beta 0.9+/-0.2 0.5+/-0.2 **

Air Filter-A3 6/6/05 Beta 0.5+/-0.2 0.6+/-0.2 **

Air Filter-A4 6/6/05 Beta 0.9+/-0.2 1.1+/-0.2 **

Air Filter-A5 6/6/05 Beta 1.0+/-0.2 1.0+/-0.2 **

Air Filter-SFA1 6/6/05 Beta 0.8+/-0.2 0.8+/-0.2 **

Air Filter-SFA2 6/6/05 Beta 0.9+/-0.2 1.1+/-0.2 **

Air Filter-SFA3 6/6/05 Beta 1.1+/-0.2 1.1+/-0.2 **

Air Filter-SFA4 6/6/05 Beta 0.7+/-0.2 0.8+/-0.2 **

Air Iodine-Al 6/6/05 1-131 <1.2 <1.4 **

Air lodine-A2 6/6/05 1-131 <1.7 <2.0 **

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

47

TABLE C Continued Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split And Location Date Analysis Analysis Analysis Analysis l0o pCi/m3 Air Filters-Al 6/15/05 Gamma <MDA <MDA <MDA Air Filters-A2 6/15/05 Gamma <MDA <MDA <MDA Air Filters-A3 6/15/05 Gamma <MDA <MDA <MDA Air Filters-A4 6/15/05 Gamma <MDA <MDA <MDA Air Filters-A5 6/15/05 Gamma <MDA <MDA <MDA Air Filters-SFAI 6/15/05 Gamma <MDA <MDA <MDA Air Filters-SFA2 6/15/05 Gamma <MDA <MDA <MDA Air Filters-SFA3 6/15/05 Gamma <MDA <MDA <MDA Air Filters-SFA4 6/15/05 Gamma <MDA <MDA <MDA mR/90 Days DR05 6/30/05 TLD 12.28+/-0.43 11.37+/-0.87 **

DR06 6/30/05 TLD 9.94+/-1.01 9.62+/-0.35 **

DR07 6/30/05 TLD 10.16+/-0.58 10.02+/-1.08 **

DR08 6/30/05 TLD 14.58+/-1.33 14.38+/-1.61 **

DRO9 6/30/05 TLD 11.14+/-1.62 10.52+/-0.91 **

DRIO 6/30/05 TLD 10.59+/-1.08 10.32+/-0.89 **

DR11 6/30/05 TLD 10.41+/-0.66 10.81+/-1.14 **

DR29 6/30/05 TLD 14.23+/-0.99 14.22+/-1.42 **

DR31 6/30/05 TLD 14.56+/-1.71 15.46+/-1.13 **

SFDR14 6/30/05 TLD 16.21+/-2.75 16.60+/-2.32 **

SFDR15 6/30/05 TLD 20.56+/-2.83 18.75+/-3.25 **

3 102 pCi/M Air Filter-Al 7/11/05 Beta 1.4+/-0.2 1.5+/-0.2 **

Air Filter-A2 7/11/05 Beta 0.5+/-0.2 0.4+/-0.2 **

Air Filter-A3 7/11/05 Beta 0.6+/-0.2 0.6+/-0.2 **

Air Filter-A4 7/11/05 Beta 1.1+/-0.2 1.0+/-0.2 **

Air Filter-A5 7/11/05 Beta 1.6+/-0.3 1.2+/-0.2 **

Air Filter-SFAI 7/11/05 Beta 1.5+/-0.2 1.4+/-0.2 **

Air Filter-SFA2 7/11/05 Beta 1.6+/-0.2 1.5+/-0.2 **

Air Filter-SFA3 7/11/05 Beta 1.2+/-0.2 1.5+/-0.2 **

Air Filter-SFA4 7/11/05 Beta 1.3+/-0.2 1.1+/-0.2 **

Air lodine-A3 7/11/05 1-131 <1.7 <1.7 **

Air lodine-A4 7/11/05 1-131 <1.9 <1.4

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

48

TABLE C Continued Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split And Location Date Analysis Analysis Analysis Analysis pCUiL Bay Water-Wa2 8/1/05 Gamma <MDA <MDA <MDA 10-2 pCi/m3 Air Filter-Al 8/8/05 Beta 2.9+/-0.3 2.8+/-0.3 Air Filter-A2 8/8/05 Beta 0.8+/-0.3 0.8+/-0.3 Air Filter-A3 8/8/05 Beta 0.8+/-0.2 0.9+/-0.2 Air Filter-A4 8/8/05 Beta 2.4+/-0.3 2.6+/-0.3 Air Filter-A5 8/8/05 Beta 2.6+/-0.2 2.7+/-0.3 Air Filter-SFA1 8/8/05 Beta 4.2+/-0.7 4.2+/-0.7 Air Filter-SFA2 8/8/05 Beta 1.1+/-0.2 1.1+/-0.2 **

Air Filter-SFA3 8/8/05 Beta 3.3+/-0.3 3.6+/-0.3 Air Filter-SFA4 8/8/05 Beta 1.9+/-0.2 1.8+/-0.2 **

Air Iodine-Al 8/8/05 1-131 <1.3 <1.5 Air lodine-A2 8/8/05 1-131 <2.0 <2.3 pCi/kg Fish-lal 8/23/05 Gamma <MDA <MDA <MDA Oysters-la3 8/23/05 Gamma <MDA <MDA <MDA pCi /kg Vegetation-lbi 8/29/05 Gamma <MDA <MDA **

Vegetation-lb3 8/29/05 Gamma <MDA <MDA **

Vegetation-lb4 8/29/05 Gamma <MDA <MDA **

Vegetation-lb6 8/29/05 Gamma <MDA <MDA **

Vegetation-lb7 8/29/05 Gamma <MDA <MDA **

Vegetation-lb9 8/29/05 Gamma <MDA <MDA **

pCVkg Soil-SFS1 9/5/05 Gamma <MDA <MDA **

Soil-SFS2 9/5/05 Gamma 135+/-8 76+/-4 107+/-21 Soil-SFS4 9/5/05 Gamma <MDA <MDA <MDA Vegetation-SFb1 915/05 Gamma <MDA <MDA <MDA Vegetation-SFb2 9/5/05 Gamma <MDA <MDA <MDA

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

49

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 lodine-A3 9/5/05 1-131 <1.7 <1.6 **

Air lodine-A4 9/5/05 1-131 <1.7 <1.4 **

Air Filter-Al 9/5/05 Beta 2.0+/-0.2 1.5+/-0.2 Air Filter-A2 9/5/05 Beta 0.5+/-0.2 0.5+/-0.2 **

Air Filter-A3 9/5/05 Beta 0.6+/-0.2 0.7+/-0.2 **

Air Filter-A4 9/5/05 Beta 1.7+/-0.2 1.5+/-0.2 **

Air Filter-A5 9/5/05 Beta 1.6+/-0.2 1.4+/-0.2 **

Air Filter-SFA1 9/5/05 Beta 1.3+/-0.2 1.5+/-0.2 **

Air Filter-SFA2 9/5/05 Beta 1.5+/-0.2 1.7+/-0.2 **

Air Filter-SFA3 9/5/05 Beta 1.6+/-0.2 1.7+/-0.2 **

Air Filter-SFA4 9/5/05 Beta 1.4+/-0.2 1.4+/-0.2 **

pCi /kg Vegetation-lb4 9/26/05 Gamma <MDA ** <MDA Vegetation-lb5 9/26/05 Gamma <MDA ** <MDA Vegetation-lb6 9/26/05 Gamma <MDA ** <MDA Vegetation-lb7 9/26/05 Gamma <MDA ** <MDA Vegetation-lb8 9/26/05 Gamma <MDA ** <MDA Vegetation-1b9 9/26/05 Gamma <MDA ** <MDA 3

10-2 pCi/m Air Iodine-Al 10/3/05 1-131 <1.2 <1.4 **

Air lodine-A2 10/3/05 1-131 <1.4 <1.5 **

Air Filter-Al 10/3/05 Beta 1.7+/-0.2 1.6+/-0.2 **

Air Filter-A2 10/3/05 Beta 1.7+0.2 1.6+/-0.3 **

Air Filter-A3 10/3/05 Beta 1.1+/-0.2 1.1+/-0.2 **

Air Filter-A4 10/3/05 Beta 1.8+/-0.2 1.8+/-0.2 **

Air Filter-A5 10/3/05 Beta 1.7+/-0.2 1.5+/-0.2 **

Air Filter-SFAI 10/3/05 Beta 1.7+/-0.2 1.5+/-0.2 **

Air Filter-SFA2 10/3/05 Beta 1.6+/-0.2 1.4+/-0.2 **

Air Filter-SFA3 10/3/05 Beta 1.8+/-0.2 1.8+/-0.2 **

Air Filter-SFA4 10/3/05 Beta 1.5+/-0.2 1.4+/-0.2 **

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

50

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 Oyster-la3 10/27/05 Gamma <MDA <MDA <MDA pCi/L Bay Water-Wa2 10/28/05 Gamma <MDA <MDA <MDA 11/29/05 Gamma <MDA <MDA **

10-2 pCi/M 3 Air Filter-Al 11/7/05 Beta 3.0+/-0.2 3.0+/-0.2 **

Air Filter-A2 11/7/05 Beta 1.3+/-0.2 2.2+/-0.2 **

Air Filter-A3 11/7/05 Beta 2.0+/-0.2 2.1+/-0.2 **

Air Filter-A4 11/7/05 Beta 1.2+/-0.1 1.3+/-0.1 **

Air Filter-A5 11/7/05 Beta 2.7+/-0.2 3.0+/-0.2 **

Air Filter-SFAI 11/7/05 Beta 3.0+/-0.3 3.4+/-0.3 **

Air Filter-SFA2 11/7/05 Beta 2.4+/-0.2 2.3+/-0.2 **

Air Filter-SFA3 11/7/05 Beta 2.8+/-0.2 3.1+/-0.2 **

Air Filter-SFA4 11/7/05 Beta 2.6+/-0.2 2.5+/-0.2 **

Air lodine-A3 11/7/05 1-131 <1.2 <1.3 **

Air Iodine-A5 11/7/05 1-131 <1.3 <1.3 **

10-2 pCi/m3 Air Filter-Al 12/5/05 Beta 2.0+/-0.3 2.3+/-0.2 **

Air Filter-A2 12/5/05 Beta 1.6+/-0.2 1.8+/-0.2 **

Air Filter-A3 12/5/05 Beta 1.3+/-0.2 1.6+/-0.2 **

Air Filter-A4 12/5/05 Beta 2.4+/-0.3 2.6+/-0.1 **

Air Filter-A5 12/5/05 Beta 3.1+/-0.2 3.1+/-0.3 **

Air Filter-SFAI 12/5/05 Beta 2.1+/-0.2 2.4+/-0.2 **

Air Filter-SFA2 12/5/05 Beta 1.8+/-0.2 1.9+/-0.2 **

Air Filter-SFA3 12/5/05 Beta 1.8+/-0.2 1.8+/-0.2 **

Air Filter-SFA4 12/5/05 Beta 1.9+/-0.2 2.0+/-0.2 **

Air Iodine-Al 12/5/05 1-131 <1.8 <1.6 **

Air lodine-A2 12/5/05 1-131 <1.1 <1.1 **

    • The nature of these samples precluded splitting them with an independent laboratory 51

TABLE C Continued Results of Quality Assurance Program Sample Type Sample Type of Original Replicate Split And Location Date Analysis Analysis Analysis Analysis o,3 pCi/M 3 Air Filters-Al 12/15/05 Gamma <MDA <MDA <MDA Air Filters-A2 12/15/05 Gamma <MDA <MDA <MDA Air Filters-A3 12/15/05 Gamma <MDA <MDA <MDA Air Filters-A4 12/15/05 Gamma <MDA <MDA <MDA Air Filters-A5 12/15/05 Gamma <MDA <MDA <MDA Air Filters-SFAI 12/15/05 Gamma <MDA <MDA <MDA Air Filters-SFA2 12/15/05 Gamma <MDA <MDA <MDA Air Filters-SFA3 12/15/05 Gamma <MDA <MDA <MDA Air Filters-SFA4 12/15/05 Gamma <MDA <MDA <MDA DR05 12/31/05 TLD 11.67+/-0.90 12.10+/-1.02 DR06 12/31/05 TLD 10.01+/-0.68 10.92+/-1.12 DR07 12/31/05 TLD 10.13+/-0.54 11.14+/-1.59 DR08 12/31/05 TLD 14.93+/-1.53 14.89+/-1.10 DRO9 12/31/05 TLD 11.38+/-0.69 11.57+/-2.64 DR10 12/31/05 TLD 10.48+/-1.01 10.85+/-1.99 DR11 12/31/05 TLD 10.77+/-0.69 11.55+/-1.86 SFDR14 12/31/05 TLD 16.37+/-2.64 18.61+/-3.05 SFDRI5 12/31/05 TLD 19.88+/-3.12 24.52+/-2.63

    • The nature of these samples precluded splitting them with an independent laboratory 52

January 1 - December 31, 2005 Docket No. 50-244 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 10-3pCi/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-11Om 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 53

January 1 - December 31, 2005 Docket No. 50-244 APPENDIX D Land Use Survey Appendix D contains the results of a Land Use Survey conducted around Ginna Station during this operating period. A table listing the raw data of this survey and a discussion of the results are included in this appendix.

Table D 1 Sector Distance to Distance to Distance to Milk Nearest Nearest Garden Producing Residence Animals E 1260 m N/A N/A ESE 1050 m Onsite Garden N/A SE 610 m N/A 8270 m SSE 660 m N/A N/A S 1560 m N/A N/A SSW 760 m N/A N/A SW 660 m N/A 4680 m WSW 1350 m N/A N/A W 1160 m N/A N/A Discussion A Land Use Survey was conducted to identify, within a distance of 5 miles, the location of the nearest milk animal, the nearest residence, and the nearest garden greater than 50 m2 in each of the nine sectors over land. A detailed description of the Land Use Survey is given in a separate document (Ref. 9). The position of the nearest residence and garden and animals producing milk for human consumption in each sector out to 5 miles is given in the above Table DI.

The closest residence is situated in the SE sector (61 Om), the nearest garden is in the ESE sector (1050 m), And the nearest milk producing animals was in the SW sector (4680m).

Changes from Previous Years:

0 Development of single family homes is increasing over past years.

Interviews with area farmers indicate that the number of acres fanned will continue to decrease.

0 No new agricultural land use was noted.

No new food producing facilities were noted.

Milk Animal Locations:

0 Gerber Farm - 450 Boston Road, Ontario, NY 0 Eaton Farm -- 6747 Salmon Creek Road, Williamson, NY No new milk producing animals were identified in the 2005 Census.

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