Text

Annual Radioactive Effluent Release Report for 2005, and Annual Radiological Environmental Operating Report for 2005
	ML061360471
Person / Time
Site:	Beaver Valley
Issue date:	05/01/2006
From:	Lash J; FirstEnergy Nuclear Operating Co
To:	; Document Control Desk, Office of Nuclear Reactor Regulation
References
	L-06-079
	Download: ML061360471 (148)
	v • d • e

FENOC AWErwW uc~ar Operatk: cwpan James H. Lash 724-682-5234 Site Vice President Fax: 724-643-8069 May 1, 2006 L-06-079 U. S. Nuclear Regulatory Commission Attention: Document Control Desk Washington, DC 20555-0001

Subject:

Beaver Valley Power Station, Unit Nos. 1 and 2 BV-1 Docket No. 50-334, License No. DPR-66 BV-2 Docket No. 50412, License No. NPF-73 Annual Radioactive Effluent Release Report for 2005, and Annual Radiological Environmental Operating Report for 2005 In accordance with Beaver Valley Nuclear Power Station Units No. 1 and 2 (BVPS)

Technical Specifications, FirstEnergy Nuclear Operating Company (FENOC) hereby submits the BVPS Annual Radiological Environmental Operating Report and Annual Radiological Effluent Release Report for 2005. These reports are provided in a single enclosure, introduced by an Executive Summary that addresses implementation of the Radioactive Effluent Control Program and Radiological Environmental Monitoring Program at BVPS in 2005. The program results demonstrate the proficiency of radioactive effluent control at BVPS, and that the operations of Unit 1 and Unit 2 did not adversely affect the surrounding environment.

The 2005 Annual Radioactive Effluent Release Report (ARERR) for BVPS Units 1 and Unit 2 is submitted in accordance with the requirements of Unit 1 and Unit 2 Technical Specification 6.9.3. The report contains the information required by NRC Regulatory Guide 1.21, along with site specific information required by Unit 1 and Unit 2 Offsite Dose Calculation Manual procedure 1/2-ODC-3.03, Attachment U, Report 6.9.3. The report format incorporates the following considerations.

The ARERR is considered a single submittal for the two-unit site.

The ARERR combines those sections that are common to both units at the site.

Therefore, since Unit 1 and Unit 2 have shared radwaste systems for elevated level gaseous effluents and shared radwaste systems for all liquid effluents, then the ARERR combines those sections.

Beaver Valley Power Station, Unit Nos. 1 and 2 Annual Radioactive Effluent Release Report for 2005, and Annual Radiological Environmental Operating Report for 2005 L-06-079 Page 2

The ARERR segregates those sections that are specific to each unit. Therefore, since Unit 1 and Unit 2 have independent radwaste systems for ground level gaseous effluents, then the ARERR segregates those sections.

The 2005 Annual Radiological Environmental Operating Report (AREOR) for BVPS Units 1 and 2 is submitted in accordance with Unit 1 and Unit 2 Technical Specification 6.9.2. The report also contains site-specific information required by Unit 1 and Unit 2 Offsite Dose Calculation Manual Procedure 1/2-ODC-3.03, Attachment T, Report 6.9.2.

No new regulatory commitments are contained in this submittal. If there are any questions or if additional information is required, please contact Mr. Gregory A. Dunn, Manager - FENOC Fleet Licensing, at (330) 315-7243.

Sincerely, James H. Lash Enclosure c: Mr. T. G. Colburn, NRR Senior Project Manager Mr. P. C. Cataldo, NRC Senior Resident Inspector Mr. S. J. Collins, NRC Region I Administrator

Beaver Valley Power Station, Unit Nos. 1 and 2 Annual Radioactive Effluent Release Report for 2005, and Annual Radiological Environmental Operating Report for 2005 L-06-079 Page 3 c: American Nuclear Insurers 95 Glastonbury Boulevard Glastonbury, CT 06033 Department of Environmental Protection (5 copies)

Bureau of Radiation Protection & Toxicology P.O. Box 2063-Harrisburg, PA 17120 INPO (Attn: Bill Nestel) 700 Galleria Parkway SE Suite 100 Atlanta, GA 30339-5957 J. Lee Miller, Beaver County Extension Director Daniel V. Steen, FirstEnergy Environmental Department John P. Jones, Hancock County Office of Emergency Services Roger L. Suppes, Ohio Department of Health Carol O'Claire, Ohio Emergency Management Agency Keith Clark, East Liverpool Water Authority Jerry Schulte, ORSANCO B. F. Jones Memorial Library Bronia Grob, Environmental, Inc.

Ron Dinello, Environmental, Inc

Beaver Valley Power Station, Unit Nos. 1 and 2 Annual Radioactive Effluent Release Report for 2005, and Annual Radiological Environmental Operating Report for 2005 L-06-079 Page 4 bc: (with Enclosures)

BVPS Chemistry Environmental Supervisor BVPS Chemistry RETS Administrator (10 copies)

BVPS Chemistry REMP Administrator (15 copies)

BVPS Chemistry Manager BVPS Regulatory Compliance (2 copies)

BVPS Quality Services Unit D. W. Jenkins J. J. Hagan Perry NPP RETS Administrator Perry NPP REMP Administrator Davis-Besse RETS Administrator Davis-Besse REMP Administrator BVPS Document Control RTL A9.690E BVRC - Keywords: Annual Radioactive Effluent Release Report, Annual EnvirownentalReport

References:

BVBP-SITE-0016 Report #31 BVBP-SITE-0016 Report #38

RTL# A9.690E FIRSTENERGY NUCLEAR OPERATING COMPANY BEAVER VALLEY POWER STATION 2005 ANNUAL RADIOACTIVE EFFLUENT RELEASE REPORT AND 2005 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT UNITS NO. 1 AND 2 LICENSES DPR-66 AND NPF-73

Executive Summary for Year 2005 Annual Radioactive Effluent Release and Annual Radiological Environmental Overating Reuorts L Overall Surmmary of BVPS Effluent and Environmental Proarams:

Report Submittal: The attached documents represent a combined submittal comprised of the Annual Radioactive Effluent Release Report (ARERR), and the Annual Radiological Environmental prating Report (AREOR). The ARERR (also referred to as the Annual RETS Report) is provided as Enclosure 2. The AREOR (also referred to as the Annual REMP Report) is provided as Enclosure 3.

This report is comprised of results from the RETS and REMP programs that are described in the BVPS Unit 1 and Unit 2 Offsite Dose Calculation Manual (ODCM) and are summarized as follows:

RETS Program and Report Results: The Controls for the Radiological Effluent Technical Specification (RETS) Program are outlined in ODCM procedure 1t2-ODC-3.03, Controlsfor RETS andREMP Programs. The RETS Controls were followed throughout the report period. Adherence to the RETS Controls (e.g.; sampling, analysis and offsite dose projection requirements), along with adherence to more restrictive Administrative Controls delineated in site implemeningprocedures, demonstrate the proficiency of radioactive effluent control at BVPS. Also, results of the sample analyses, coupled with the offsite dose projections demonstrate that BVPS operations should not produce any adverse affect on the surrounding environment.

REMP Promram and Report Results: The Controls for the Radiological Environmental Monitoring Brogram (REMP) are outlined in ODCM procedure 1/2-ODC-3.03, Controlsfor RETS andREUP Programs. The REMP Controls were followed throughout the report period. Adherence to the REMP Controls (e.g.; sampling and analysis requirements) demonstrated the proficiency of radiological environmental monitoring. Also, results of the various environmental sample media validate the offsite dose projections made in accordance with the RETS Controls. In summary, the results demonstrate that BVPS operations did not adversely affect the surrounding environment

Executive Summary for Year 2005 Annual Radioactive Effluent Release and Annual Radiological Environmental Operating Reports II: Detailed Summary of Enclosure 2 - Annual RETS Report (ARERR) for 2005:

Report Submittal and Requirements: The ARERR was prepared and submitted in accordance with the requirements contained in the following documents:

BVPS Unit 1 Technical Specifications, Administrative Control 6.9.3

BVPS Unit 2 Technical Specifications, Administrative Control 6.9.3

NUREG-1301, "Offsite Dose CalculationManual Guidance:StandardRadiologicalEffluent ControlsforPressurizedWater Reactors, GenericLetter 89-01, SupplementNo.), April 1991"

Regulatory Guide 1.21, "MeasuringEvaluatingandReporting Radioactivity in Solid Wastes andReleases ofRadioactiveMaterialin Liquid and GaseousEffluentsfom Light-Water Cooled Nuclear PowerPlants, Revision 1, June 1974"

ODCM procedure 1t2-ODC-3.03, "ControlsforRES andREMP Programs",Attachment U, Control 6.9.3

BVPS procedure 112-ENV-01.05, "Compliancewith Regulatoiy Guide 1.21 and Technical Specifications"

BVPS Condition Report No. CR05-03558-02: Provide description ofAbnormal Liquid Release in the ARERR for 2005 2

Executive Summary for Year 2005 Annual Radioactive Effluent Release and Annual Radiological Environmental Operatinm Reports Summary of the BVPS RETS Program for Liquid and Gaseous Effluent Control

Trends of Total Dose: The following graph provides a comparison of the ODCM dose projections from all facility releases and direct radiation exposures to show compliance with Member of the Public dose limits from 10 CFR 20.1302 and 40 CFR Part 190. The graph reflects the results of the efforts to stabilize and reduce offsite dose.

40 CFR 190.10(a) 1.000 mrem = Total Body Dose, or 4.01% of the 25 mrem annual limit 40 CFR 190.10(a) 0.967 mrem = Thyroid Dose, or 1.29 % of the 75 mrem annual limit 10 CFR 20.1302 3.85 mrem = Total Effective Dose Equivalent, or 3.85% of the 100 mrem annual limit Unit l and Unit 2 Total Dosel 100.0%

,E 10.0%

I 10 0 1.% 0 0 1 ULnit 1&2, Percent of 40 CFR 190.10(a) Total Body Dose Linit 0 Lnit 1&2, Percent of 40 CFR190.10(a) Thyroid Dose Linit

- Unit 1&2, Percent of 10 CFR 20.1301 (a)(1) TEDE Dose Un-it 3

GoI

Executive Summary for Year 2005 Annual Radioactive Effluent Release and Annual Radiological Environmental Operating Reports

Trends of Offsite Dose: The graphs on the following pages provide a comparison of ODCM dose projections for the last several years to show compliance with Members of the Public dose limits from 10 CFR Part 50.

Total Population Dose vs Natural

Background:

The 0-50 mile total and average population doses were calculated using liquid and gaseous release quantities and real time meteorology. The average population dose is based on 4 million people within 0-50 miles of the BVPS site. The following comparison to natural background radiation demonstrates that BVPS operations did not adversely affect the surrounding environment:

1238 man-mrem =BVPS Total Population Dose for the year 0.0003096 mrem = BVPS Average Individual Dose for the year 296 mrem = Natural Background Individual Dose for the year. This dose value is documented as natural background radiation exposure for an individual in a year from the 1990 BEIR V Report.

Liquid Release Volume: Unit 1 and Unit 2 discharged 6,650,000 liters of liquid waste.

Liquid Release Activity (Excluding Tritium): The total mixed fission and activation product (particulate) radioactivity discharged from the site was 0.424 Curies.

4

Executive Summarv for Year 2005 Annual Radioactive Effluent Release and Annual Radiological Environmental Operating Reports

Liquid Release Tritium Activity: The total tritium radioactivity discharged from the site was 2450 Curies.

Liquid Tritium Inventory Reduction: In July 2004, the site initiated an Action Plan to reduce the site liquid tritium inventory. This effort will ensure future offsite dose (due to evaporation of tritiated water from the spent fuel pools) is reduced. The following graph shows progress made toward the reduction of site liquid tritium inventory.

Site Liquid Tritium Inventory Reduction 12000 -

10000 -

T 8000 -

6000 -

4000-

-l Site Total 2000 -

0-QP? QPc Qc 5

tc-c3

Executive Summary for Year 2005 Annual Radioactive Effluent Release and Annual Radiolodical Environmental Operatin2 Reports

Liquid Release Offsite Dose Proiections: The following offsite dose projections were calculated to the maximum individual per 10 CFR 50, Appendix I and the ODCM. The projections use ODCM default flow rates for the receiving water (Ohio River). The projections were performed prior to release authorization, and are summarized as follows:

10 CFR Part 50, Appendix I 0.0438 mrem = Unit 1 Total Body Dose, or 1.460% of the 3 mrem annual limit 10 CFR Part 50, Appendix I 0.0620 mrem = Unit 1 Highest Organ Dose, or 0.6196% of the 10 mrern annual limit 10 CFR Part 50, Appendix I 0.0438 mrem = Unit 2 Total Body Dose, or 1.460 % of the 3 mrem annual limit 10 CFR Part 50, Appendix I 0.0620 mrem = Unit 2 Highest Organ Dose, or 0.6196% of the 10 mrem annual limit Unit 1 or Unit 2 Liquid Effluent Dosel 100.0% l 10.0%

00 0.1%

-N Unit 1 or Unit 2, Percent of Maximum Organ Dose Uirnit 0 Unit I or Unit 2, Percent of Total Body Dose Lirrit 6

Executive Summary for Year 2005 Annual Radioactive Effluent Release and Annual Radiological Environmental Operating Reports

Liquid Radwaste Treatment Svtstem: The BVPS site operates with the concept of a shared Liquid Radwaste Treatment System, even though each Unit has its own system of ion-exchange vessels. Using this concept allowed either Unit to process liquid waste at the Unit of origin, or at the other Unit. Typically, when Unit 1 or Unit 2 high level liquid waste was processed (e.g.; coolant recovery waste) it was performed at Unit 1, because that system has an additional carbon pre-conditioning filter (50 cubic feet).

Abnormal Liquid Releases: There was 1 abnormal liquid release during the report period.

In accordance with Technical Specification 6.9.3, ODCM procedure 1/2-ODC-3.03, Attachment U Control 6.9.3, and procedure 1/2-ENV-01.05, the Unplanned Release of 326 micro Curies of Fission Action Products from the Unit 1 Sewage Treatment Plant to the Ohio River was an Abnormal Release. This unplanned release was quantified via RWDA-L-5026, and consisted of Manganese-54 = 10 micro Curies, Cobalt-58 = 219 micro Curies, Cobalt-60 = 53 micro Curies and Zirconium/Niobium-95 = 44 micro Curies. The Offsite Dose consequence for this release was negligible in comparison to ODCM Limits. The Total Body Dose was 0.00248 mrem, and the Highest Organ (Liver) Dose was 0.0442 mrem. This condition and associated Corrective Actions are documented in Condition Report CR05-03558.

Gaseous Release Activity: The total radioactivity discharged from all site gaseous releases was 0.857 Curies of fission and activation gases, no detectable Iodine-131, 0.0000246 Curies of particulates with half-lives >8 days, no detectable gross alpha, and 55.6 Curies of tritium.

7 U-

Executive Summary for Year 2005 Annual Radioactive Effluent Release and Annual Radiolovical Environmental Operatin2 Reports

Gaseous Radwaste Treatment System: The BVPS site operates with the concept of a shared Gaseous Radwaste Treatment System, even though each Unit has its own system of charcoal delay beds and storage/decay tanks. Using this concept allowed either Unit to process gaseous waste at the Unit of origin, or at the other Unit. Typically, when Unit 1 or Unit 2 went to a shutdown condition, the gaseous waste was sent for storage and decay at Unit 2 because that system has 4 additional storage tanks.

8

Executive Summary for Year 2005 Annual Radioactive Effluent Release and Annual Radiological Environmental Operatin2 Reports

Unit 1 Gaseous Release Offsite Dose Projections: The following offsite dose projections were calculated to the maximum individual per 10 CFR 50, Appendix I and the ODCM. The projections use ODCM default meteorological parameters for the atmospheric conditions surrounding the plant site. The offsite dose projections during the report period were performed prior to release authorization, and are summarized as follows:

10 CFR Part 50, Appendix I

<0.00001 mrad = Unit 1 Gamma Air Dose, or

<0.0001% of the 10 mrad annual limit 10 CFR Part 50, Appendix I

<0.00001 mrad = Unit 1 Beta Air Dose, or

<0.0001% of the 20 mrad annual limit 10 CFR Part 50, Appendix I 0.443 mrem = Unit 1 Highest Organ Dose, or 2.9507% of the 15 mrem annual limit Unit 1 Gaseous Effluent Dose 100.00%

10.00%

2-1.00%

0 0.10%-00 EUnit 1, Percent of Garnra Air Dose Lint

' Unit 1, Percent of Beta Air Dose Linit Unit 1, Percent of mighest Organ Dose Linit 9

coi

Executive Summary for Year 2005 Annual Radioactive Effluent Release and Annual Radiolo2ical Environmental Overating Reports

Unit 2 Gaseous Release Offsite Dose Proiections: The following offsite dose projections were calculated to the maximum individual per 10 CFR 50, Appendix I and the ODCM. The projections use ODCM default meteorological parameters for the atmospheric conditions surrounding the plant site. The offsite dose projections during the report period were performed prior to release authorization, and are summarized as follows:

10 CFR Part 50, Appendix I 0.000025 mrad = Unit 2 Gamma Air Dose, or 0.0003 % of the 10 mrad annual limit 10 CFR Part 50, Appendix I 0.000073 mrad = Unit 2 Beta Air Dose, or 0.0004% of the 20 mrad annual limit 10 CFR Part 50, Appendix I 0.0812 mrem = Unit 2 Highest Organ Dose, or 0.5413% of the 15 mrem annual limit Unit 2 Gaseous Effluent Dosel 100.0000000%

10.0000000% 1 1.0000000%

E 0.1000000%

0 00100000%

.000o1000o% '-f 0.00001 00%

0.0000010%

0.0000001%

_ Unit 2, Percent of Gartia Air Dose Linit o Unit 2, Percent of Beta Air Dose Lirrit Unit 2, Percent of Highest Organ Dose Linit 10 COT

Executive Summary for Year 2005 Annual Radioactive Effluent Release and Annual Radiological Environmental Operating Reports

Abnormal Gaseous Releases: There were no abnormal gaseous releases during the report period.

Effluent Monitoring Channels Inoperable >30 Days: There were no Effluent Monitoring Instrumentation Channels not returned to Operable status within 30 days during this report period.

ODCM Surveillance Deficiencies: There were no ODCM Surveillance Deficiencies during the report period. This is regarding all ODCM required Surveillances for monitoring, sampling & analysis and offsite dose projection

ODCM Changes: There were no changes made to the ODCM during the report period.

11

Executive Summary for Year 2005 Annual Radioactive Effluent Release and Annual Radiological Environmental Operating Reports III. Detailed Summary of Enclosure 3 - Annual REMP Report (AREOR) for 2005:

Report Submittal and Requirements: The AREOR was prepared and submitted in accordance with the requirements contained in the following documents:

Unit 1 Technical Specifications, Administrative Control 6.9.2

Unit 2 Technical Specifications, Administrative Control 6.9.2

NUREG-1301, "Offsite Dose CalculationManual Guidance: StandardRadiological Effluent Controlsfor Pressurized WaterReactors, Generic Letter 89-01, Supplement No.1, April 1991"

Regulatory Guide 1.21, "Measuring Evaluating and ReportingRadioactivity in Solid Wastes and Releases of Radioactive Material in Liquid and Gaseous Effluents from Light-Water CooledNuclear Power Plants, Revision 1, June 1974"

ODCM procedure 1/2-ODC-3.03, Attachment T, Control 6.9.2, "Controlsfor RETS and REMP Programs"

BVPS procedure 1/2-ENV-01.05, "Compliance with Regulatory Guide 1.21 and Technical Specifications"

BVPS procedure 1/2-ENV-02.01, "Descriptionof OverallRadiologicalEnvironmental Monitoring Program"

BVPS Condition Report No. CR05-05888-01: Provide information in AREOR to indicate that REMP air particulate and radioiodine sample stations were upgraded from 8 ampere trip circuits to 15 ampere trip circuits.

BVPS Condition Report No. CR05-07299-01: Provide results of the 2005 Land Use Census in the AREOR for 2005

BVPS Condition Report No. CR06-00050-01: Provide reasons for missing environmental sample results in the AREOR for 2005 Summary of the BVPS REMP Program for Determination of Environmental Impact

Sample Media and Analyses: Results for precipitation, ground water, sediment, food, fish, TLDs, feed crop, food crop, air particulate and air radioiodine media remained consistent with previous years data. Minor increases and decreases were noted. All positive results attributable to the BVPS operation were consistent with station data of authorized radioactive discharges and were within limits permitted by the NRC license and the ODCM.

Other radioactivity detected was attributable to naturally occurring radionuclides, previous nuclear weapons tests, other man-made sources, and to the normal statistical fluctuation for activities near the Lower Limit of Detection (LLD). With exception to identification of Cobalt-58 and Cobalt-60 in the sediment at the outfall facility, the pre-operational values were not exceeded during the report period.

12

Executive Summary for Year 2005 Annual Radioactive Effluent Release and Annual Radiological Environmental Operating Reports

Missing Environmental Sample Results: The ten air particulate filters for the week of 10/03/05 through 10/10/05 were misplaced by the contractor laboratory prior to analysis for gross beta. The gross beta data results for this week-were determined by assuming an average from the previous and the following weeks. This condition and associated Corrective Actions are documented in Condition Report No. CR05-00050-01.

Upgrading Trip Circuits for Air Particulate and Radioiodine Sample Stations: During the report period, the ten air particulate and radioiodine sample stations were upgraded from 8 ampere trip circuits to 15 ampere trip circuits. This condition and associated Corrective Actions are documented in Condition Report No. CR05-05888-01.

Population Dose - Liguid Releases: The calculated 0-50 mile population dose from liquid releases was 942 man-mrem. This population dose compares favorably to the 1704 man-mrem dose for the previous year.

Population Dose - Gaseous Releases: The calculated 0-50 mile population dose from gaseous releases was 296 man-mrem. This population dose compares favorably to the 316 man-miern. dose for the previous year.

Land Use Census Results: Highlights from the most recent Land Use Census are documented in Condition Report No. CR05-07299-01, and shown as follows:

1) The nearest resident has not changed since the previous census. The location is at 211 Ferry Hill Road, Shippingport, PA (0.406 miles NE).

2) The nearest garden >500 square feet has changed since the previous census. The previous location was at 158 Morrow Drive, Shippingport, PA (1.028 miles ENE). The current location is at 238 State Route 168, Hookstown, PA (0.760 miles SSW).

3) The nearest dairy cow milked has not changed since the previous census. The location is still at Searight Dairy, 948 McCleaxy Road, RD 1, Hookstown, PA (2.097 miles SSW).

4) The nearest doe goat milked has not changed since the previous census. The location is still at Moore Farm, 982 State Route 168, Hookstown, PA (2.120 miles SW). This is not the nearest location, but it is the nearest location providing samples.

5) The nearest beef cattle location has not changed since the previous census. The location is still at 105 Shippingport Road, Shippingport, PA (1.405 miles ENE).

6) Using the results of the 2005 Land Use Census, the 2006 dairy cow sampling locations will remain at the same locations used in 2005. The locations are; Searight Dairy, 948 McCleary Road, RD1, Hookstown, PA (2.097 miles SSW), Halstead Dairy, 104 Tellish Drive, Hookstown, PA (5.079 miles SSW), Brunton Dairy, 3681 Ridge Road, Aliquippa, PA (6.158 miles SE), and Weindsheimer Dairy, RD 1 Burgettstown, PA (10.476 miles SSW).

7) Using the results of the 2005 Land Use Census, the 2006 doe goat sampling locations will also remain at the same locations used in 2005. The locations are; Moore Farm, 982 State Route 168, Hookstown, PA (2.120 miles SW), and Collins Farm, 289 Calhoun Road, Aliquippa, PA (3.547 miles, SE).

13

Executive Summary for Year 2005 Annual Radioactive Effluent Release and Annual Radiological Environmental Operating Reports

Groundwater Monitoring: A total of six (6) offsite ground water samples were collected and analyzed for Tritium and by gamma spectrometry during the report period. The samples were collected on a semi-annual basis from three (3) locations within four (4) miles of the site. The locations included one (1) well in Shippingport, PA, one (1) well in Hookstown, PA, and one (1) well in Georgetown, PA. No gamma-emitting radionuclides were detected in the analyses. Also all tritium results were less than LLD. The following graph shows that offsite groundwater tritium is less than the pre-operational value.

Beaver Valley Power Station REM P Tritium Trends - Ground Water 100000

- Indicator Mean (pCi /1) 10000 -- -*---Control Location (pCi / 1)

Pre- Operational (300 pCi/l)

-- Required LLD (2,000 pW/l)

- Reporting Level Ground Water (30,000 pi/I)

.2 100 -- _-_-_-_-_-_-_-_-_-_-_-_-_-_-____

100 - -_-_-_-_-_-_-_-_-_-_

0 9 5 9 9 9 9: 699 9 9 9 5 9 10 , , , , , , ,, , . ,,. , , .

Split Sample Program (Inter-laboratory Comparison, Part 1 of 2): BVPS shared split sample data with the Pennsylvania Department of Environmental Protection (PADEP) in support of the nuclear power plant monitoring program. The shared media and number of locations are typically comprised of; milk (1), surface water (3), sediment (1), fish (1), food crops (2), co-located air particulate/air iodine (4), and TLD (24). SINCE the split sample program is coordinated by the state, THEN the results are not provided with this report.

Spike Sample Pro2ram (Inter-laboratory Comparison. Part 2 of 2): Spiked samples were provided by an independent laboratory and then analyzed by the REMP contractor laboratory. The samples were provided throughout the report period and included water samples, milk samples, filter paper samples and charcoal cartridge samples. All 104 analyses performed by the contactor laboratory on the spiked samples met the NRC comparison criteria.

14 cY15

RTL A9.690E Annual Radioactive Effluent Release Report (Annual RETS Report)

FirstEnergy Nuclear Operating Company FENOC Beaver Valley Power Station - Units I & 2 Unit I License No. DPR466 Unit 2 LUcense No. NPF-73 Annual Radioactive Effluent Release Report Calendar Year - 2005

Beaver Valley Power Station - Units I & 2 Annual Radioactive Effluent Release Report Calendar Year - 2005 Index

_ Supplemental Information Page 1 Table IA Gaseous Effluents - Summation Of All Releases 2 Table IB-EB Gaseous Effluents - Elevated Batch Releases 3 Table IB-EC Gaseous Effluents - Elevated Continuous Releases 4 Table IC-1B1 Gaseous Effluents - Ground Level Batch Releases (Unit 1) 5 Table ICOCI Gaseous Effluents - Ground Level Continuous Releases (Unit 1) 6 Table IC-GB2 Gaseous Effluents - Ground Level Batch Releases (Unit 2) 7 Table IC Gaseous Effluents - Ground Level Continuous Releases (Unit 2) 8 Table 2A Liquid Effluents - Summation Of Al Releases 9 Table 2B-B Liquid Effluents - Batch Releases 10 Table 26-C _iuid Effluents - Continuous Releases 11 Table 3A Solid Waste And Irradiated Fuel Shipments (Part I of 3) 12 Table 3B Solid Waste And hradiated Fuel Shipments (Part 2 of 3) 13 Table 3C Solid Waste And Irradiated Fuel Shipments (Par 3 of 3) 14 Table 4 Lower Limits Of Detectability 15 Table 5A Assessment Of Radiation Doses (Unit 1) 16 Table 5B Assessment Of Radiation Doses (Unit 2) 17 Table 6 Effluent Monitoring Instrumentaton Channels Not Retumed To Operable Status Within 30 Days 18 Table 7 Total Dose Commitments, Total Effective Dose Equivalents and Population Doses 19 Table 8 Offsite Dose Calculation Manual Surveillance Deficiencies 20 Table 9 Unit I and 2 Offslte Dose Calculation Manual Changes (Description) 21 Affapthmanl 1 AIni Vmmrn~ re fl~owidinn TahIka

. I _... . .---

Note: The Total Error values (%) listed In this report are documented In Calculation Package No. ERS-ATL-04-002

Formn 1/2-ENV-1.05.FOI (page 1 of 21). Rev I RTUA9.690E Beaver Valley Power Station - Units I & 2 Annual i.aea rea Radioactive Effluent Release~rge1~T~ Report %--- A_-Zf r

cValendar Year - ZUU5 rage -I OTC-I Supplemental Information Page M l=fIY_

l _O 1?" tI] _w n 1 O0 EMMIN Q Annual Unit i or 2 Dose' 10 mad from Gamma. & 20 mrad from Beta 1 or2 Dos: 15 maembAny Oan i or2 Oose: 3 mrem btOal Body. & lnrem o Any Owan I ImtNvr to Total Body. & 3000 mrernro bhe SIdn I Release Rate: 1500 mmenyr lAy Omgan 10Iimes 10 CFR 2DAwemdix B. Table 2. EC'sl wxm Wregional fo iI M Spedmmetr. Liquld Scntilation Counter mGamma SwectromeW Proporional Counter le Gammna SneCramtrvn. Pronoronal Counter. LUqud Sdnlation NONE I NONE I NONE I NONE I 0.002400 I QOE.O0 I O.OOE+400 I C.COSM I

Fonm 12-ENY-01.05.F01 (page 2 of 21). Rev i RTLF 0 AMDE Beaver Valley Power Station - Units I &2 Annual Radioactive Effluent Release Report Calendar Year - 2005 Page 2 of 21 Table 1A Gaseous Effluents - Summation Of All Releases 12.04E-03 8.57E-01 l 26.5%1 DO 1.0212-03 4.24E-01 00 _1.02E-03 4.33E-O1 00 2.59E-04 2.72E-02

_WNA NUA O.OOE+00 I0.0E+00I O.OOE4+00 [ 28.3%

0.00D+O O.OQE+OOI O.OOE+QO I 002+00 0.00EI+ 0.OOE+OO 0 .002+00

.OQE+OO0 O.OOE+00

= _

IO.OQE+00Q 0.OE+O I WA I NA I WA I I-0.0012+00

_ - I 0I.OOE+00 2.461-051

_ I -

30M.1Y 00E+00 0.00E+00 0I.OOE+00 O.OOE+00

+00 I 2.46E-5 0.OE+00 I0.OOE+00 2.46E-05

'00 3.12E-06 0.OOE+00 0.00E+00 7.79E-07 WA WA WA NIA 10.00E+00 O.OOE+00 0.00E+00I 30.0%1 0.00QE+OO O.oOE+00 0.00E+001 0.002+00 0.02E+00 0.OOE+00 0.00E+0070.00E+00 0.00E+00 0.00E+00 0.002+00]

WA NWA NWA WA tWA 1.26E+01

_ _ i 5.56E+01 32.B%1 1.09E+01 4.59E+01 1.70E+00 9.67E+00 1.60E+ID 1.76E+00 NWA NWA WA = Not Appricable The amount of time (in seconds) used to calculate the release rates specified in A.2, B.2, C.2, D.2 and E.2 Is the average amount of seconds per calendar quarter (7.88E+06 seconds).

Form 1/2-ENVW01.05.FOI (page 3 of 21), Rev I IW RI. 5A9.890E Beaver Valley Power Station - Units I & 2 Annual Radioactive Effluent Release Report Calendar Year - 2005 Page 3 of 21 Table 1B-EB Gaseous Effluents - Elevated Batch Releases L. LL LL LLD L SE-02 4.00E-01 LL AL 4.33E-01 LD 1.32E404 L LL 1.32E-04 LUD LD LL LW L LL LW LLD L D L

-LL LLW LLD LLD LLD LLD 3.42E.01 LIU LD 3.42E-01 LL 7.55E-03 LW LW 7.55E-03 LW tt.04E.02 LW LW 1.04E-02 LW LWD LlD LLD LW LD LLD LD L NONE NONE NONE NONE NONE 3.28E-02 I 7.60E-01 I ND I ND I 7.93E-01 L D

_LID UL - _D LD ILLD l UD LLLD _ LLD _D _ _

ND ND N___D _ ND ND NL __ _L _ _ __ L _DLD_ _ D '

L LD LWD LDL LL LLD LLW LWD LWD LWD LWD 1 LLW LDLLDD LWD LLD LDLLD ILW LWD LWD

~LWD ohLtD L ILLD LWI LLW LWD LWD LWD LWD LWD LWI LWD LWD LWD LWD LLW LW LLDW LD LWD II$ bLD 1 L LW usL LLD LLD LWD IW IDW LLLDz U LLW LD sLD LW LID W UL LWD a LL UlD LLD L LLD

_L LLD LWD LW L

-L LW Lw LLW LlD

- NONE NONE NONE NONE NONE g _$fl. ND ND ND ND ND LLD mBelow the Lower Linit of Detectability, In uCVcc (Table 4).

ND mNone Detected

Form 112-ENV-1.05.FOI (page 4 of 21), Rev I RTL WA.60E Beaver Valley Power Station - Units I & 2 Annual Radioactive Effluent Release Report Calendar Year - 2005 Page 4 of 21 Table IB-EC Gaseous Effluents - Elevated Continuous Releases LD LLDW LD UD LD LL D LLD L L DW LLD LlD l L 1 10 U I LLD LLD LlW LLD WD LLD LLD LWI LW LW LLD LD LLD LD UO. LD 1.68E42 3.55E402 UW 2ME.03 5.43E-02 LWD LL LW L LL LLD L LID U LL L LW LW LWD LL LLW LWD LW LW L NONE NONE NMNE 'ONE N NONE r.S;EBB~isnMCMA 1 ARF.0 1 a S I Ni - I 2-Dn4Ew3 I 6.n i'1 n UD I I UD LL LWD LLD LWD LL I LLD LWI L LLD ID LLD LD d 'il. ND ND [ ND ND l ND iri i LWI Lm LW LW LLD LWD LLW LWD LW

~4 LWD LWI LWI LWD LWD iJat i LWD LWD LWD LW LLD LW U LLW LWD LWD LLD LWD LWI LO LWD I w LLD LWI LLW LWD LWD

- ~ ~LWD LWD LWD LD LWD Um UD m ) UJD LD LD LWD LWD LWD LW

~ W LW LW LLW LWD LWD LWD LWD LWD LWD

~s~~~~ ~~h~LWD LWD LWD LWD LLW

~iLfe~uI~~iIiV~~ NONE NOWE NONE NOWE NONE W _ UD N ND ND ND ND LD = Below the Lower Lhfl of Detectabirdy, bI uClcc (Table 4).

ND = None Detected

Form 112-ENV-01.05.FOI (page 5 of 21), Rev I RTL #A.690E Beaver Valley Power Station - Unit I Annual Radioactive Effluent Release Report Calendar Year - 2005 Page 6 of 21 Table IC-GBI Gaseous Effluents - Ground Level Batch Releases (UnIt 1)

. LW LL LLD LL LW LLD LD LD UD LD UD LL LD LD D LW LLD LLW LWD LLD LW LL LLD LLD

UD :U LLD LLD LLD LLD LL i LW LLW LLD :L AM LWD LLn W LD LWD UD LW WLLD ~ LW LLW LW LW LWO LW LW LWD NONE NOW NONE NONE NONE

,*t: NDl ND ND ND ND 4L_______ W2 ) LLJD LLD_____ LLD___LLD LL W) i, l l EL .E.UD UiD i . 1' W Di UD LLD NDN Dl D N_ _D_ ND aE4 LLD m mtIl LLD] UID LL LLD LLD l LD WUD

_ _ L LW LLD llD LLD _D LWD un LLD

= -LeD LLL LWD UDLW LLD

_ UD llUD iM UD lIUDl ifr= itl lX lULD ;U UID L I L UD

. b h j l UD LLD D UDL W LW UDW LWD R4 1 L LW l L LUD t A LW

£C

,*'D LW LW UD UD

.U a D t UD I JsD- U 1 lD ID 3 U- l ll n l 1 UD .UD l

. 3D 1o LW U14D § LWD I LW UD LW DOM NONE I NONE I NONE NONE NONE 13&o I i% ND I D ND ND ND LlD = Below the Loer LUmt of Detectability, n uCUcc (rEble 4).

ND u None Detected

Form 1/2-4EW-01.05.FOI (page 6 of 21), Rev I RTLF#.690E Beaver Valey Power Station - Unit I Annual Radioactive Effluent Release Report Calendar Year - 2005 Page 6 of 21 Table IC-GCI Gaseous Effluents - Ground Level Continuous Releases (Unit 1)

LIW EL LLD LLD LLD LLD LLD LLD LLD L LLD LLD LLW LLD LLD LLD L,DW L LLD LLD LLW LLD LWD LWD LLD LLW LLW LLD LLD LLD LLD LLW L L L W LIW LLD LW LLD LLD LWD LWD LLW LW LW LLD LD L LWD LLD L- LW L I. NONE NONE NONE l NONE NONE

. ffi1 ND ND ND ND ND E LL1 UD l llD L LD LL 110 l LD LLD TLUD LLD LLUD LLID LL LL>D LID TLUDl LLD a i' w ND lNO I ND I ND lNDl LLDn LLD LLI IJD UD LLUD

_ WlU LjX LD LL LLD LLUD LLUD1 LLD LLD LLDLLD LL LL~i D LLD} . LLD> LLUD

~72 l LLD LWD LLD l LLUD LLD llD l

Jl LUD LLD LUD t LLD IDL.D LLUD LLD LLUD LL LLDWg5 LLD LL LL.D LL gL gLsD LLD LLD LLD LL LItD LLD LLD LLD

'LL LLttD LLD LLD LLD LLUD UMLD ULD LLD DLD LLUD LLD LLD LD LLD LLD

.gg@&~ ilUD LL LLD LD WOMM NOE I NOEINONE INONE -FNONE

_Ml oW XND I ND I ND I ND I ND LD = Below the Lower Lkn of DetectabilIty, In uClc (Table 4).

ND - None Detected

Form 112-EW-01.05.FO1 (page 7 of 21), Rev I RML#AMSOOE Beaver Valley Power Station - Unit 2 Annual Radioactive Effluent Release Report Calendar Year -2005 Page 7 of 21 Table IC-GB2 Gaseous Effluents - Ground Level Batch Releases (Unit 2)

LLD LLD LLD LLD LLW LLD LLD LD_ LLD LWD LID LD LL LL L LLD LD LL LW L LWD L_ LW LD LLD LLD LL LID LlD LD LLD LWL LW_ LD LWD L LL L LlD LlD LW LW LW llDW LlD LlD ilD UDLLD llD LLD LLD LWD LLW LLD NONE NONE NONE NONE NONE ND ND ND ND ND LWD LlD [ LD llD LWD L llD llD LLD lD LLD i LUD l 1 LLD LI ULD ND [ D ND ND ND LLD LWD LW LD LLD I LLD LJ LLW LWD LWD LlD L D LW IJW L LWD LWD LWD LWD LLD LLD 9.17E-06 LW LWD 9.17E-06 LlD 6.IE-07 LlD LlD 6.IE-07 LWD LW D LW LD LD LLDW LLD I D ;L LWD LWD LW LW LW L LW LW LL LWD L

.LID. llD UD LD L ll D LlD - IIIE.07 LWD L 6.IIE.07 ILW Ll UD _ LW LWD

,IL -L W L- -

HCmE I MUMIN I NUN IMumNON I NmNu IND . 1.04E.05 I ND ND I 1.04E-05 LWD - Below the Lower Unit of Detectability, InuCIcc (Table 4).

ND z None Detected

Form 1W2-ENV-01.05.FO1 (page 8 of 21), Rev I RnTLA9.69OE Beaver Valley Power Station - Unit 2 Annual Radioactive Effluent Release Report Calendar Year - 2005 Page 8 of 21 Table IC-GC2 Gaseous Effluents - Ground Level Continuous Releases (Unit 2)

LLD UD I UD IL LD 1.UGE-06 L_ LL 1.19E-06 LD LLD LLD LD LD LLD LD LD LDW ULD LLD LW LLW LW L LD LL LD LWD L LW S.&E03 LLD 0 LW 9.65E-03 L LW LW LWD LD LLD LLD LLW LWD LD LD _ LL LD UD LD LWD LLW LWD LWD LWD NONE NONE NON NONES NOt E ND 9.65E-03 ND ND T 9.65E-03

. _ _ _D I I LDW ND ND ND ND ND UD L WLD UDL UD LW L WD L WD LW LW iLD I I UD TUD IUDI

-LD WD UDLL ULD lW 7.57E.OB LID LWD 7.67E-0 LD 6.E-w LWD UlW 6.59E-06 L W LW LW LW LW LWD LW LW UD LW LD 'LD LUD UD UD UD LD LU LD' LWD LWD ULW LW UD UD LW LW LW LW LW L Wn LW LW LW LW II iin L

&s% I W a%7I60 W I Uo I muP4m n1 mu ' RUPMM 1 nvmr.

I 1.42E.05 I ND I ND -1.42.E.05 I LWD -Below the Lower LhUnt of Detectabirdy, In u~cc (Fable 4).

ND = None Detected

Form 12ENW-01.05.FOi (Mpae 9 of 21), Rev i RM#AS.60E Beaver Valley Power Station - Units I &2 Annual Radioactive Effluent Release Report Calendar Year - 2005 Page 9 of 21 Table 2A Lquld Effluents - Summation Of All Releases 2 1 1.32E-01 3.76E-02 2.83E-02 424E-O1 26.1%

1.84E-07 8.04E-08 2.75E-08 6.09E-08 9.24E-08

.0415+00 529E+00 1.50E+00 1.13E+00 424E+00 1.51E+03 5.A3E+02 2.38E+02 11.58E+02 2A5E+03 25.0%

1.23E-03 3.30E-04 1.74E-04 4.53E-04 5.34E-04 1.23E+01 3.30E+00 1.74E+00 4.53E+00 5.34E+00 ND 4.50E-03 ND ND 4.50E-03 27.0%

2.74E-09 ___ ___9.80E-10 1.37E-03 4.90E-04 LLD LLD L JnLD j 28.9%f 9 PYY*PhOllil999S99 PsS i i' P9EPPlic929JPl1PP ze.i11 i \!ppL9S9W9p5511ptB9!1994 iEii . 'PExiP{IiA:rlePt ili iiL:-E9aP:i iSiii pf vPP911zL9iP 2.14E406 s

2.52E+06 1.24E+06 7A8E405 6.65E+06 { 11.2%I 1.3E+0O9 1.64E.09 1.371E+09 J3A49E+08 4.58E409 22.9%j LLD Below the Lower Unit of Detectabirlty, In uClhml (Table 4)

A3 Is based on a historical PA-DEP guide of 10 Cilyr B.3 is based on a ODCM lirnit of I.OE-2 uCihMi C.3 Is based on a ODCM limit of 2.OOE-04 uCUmid The values listed at F. are the volumes during actual Ilquid waste discharge periods. The total dilution volume for a continuous calendar quarter Is approximately 1E+10 ilter for BVPS-1 & 2 (hs; - 2Z800 gpm Is the toW dilution flowrate from the site)

Fom 1n2ENvW.01S.FO e 10 oM2l RaFI RTL#Ag.690E Beaver Valley Power Station - Units I & 2 Annual Radioactive Effluent Release Report Calendar Year - 2005 Page 10 of 21 Table 28-B Llqedd Effluents - Batch Releases LW LLD LLD LL LLD LL W L. lWn LLD 3.21E-03 5.68-E04 LLD LLD 3.78E-03 9.2E-04 4.12E-04 1.73E2- LW 1.33E-03 6.87E.02 1.99E-02 0.16E-03 7.43E-03 1.05E-01 7.67E-04 1.00E03 9.12E- L- 1.86E-03 1.1725 1.24E-04 .5E4-05 1.46E-04 &17E-04 2.63E-02 522-02 1.03E-02 1.47E-02 1.04E-01 1.022-02 E.212-03 1.72E203 2.20E-03 2.13E-02 6.81E-03 2.72E-03 2.07E-04 424E-04 1.02E-02 LlD LL llD W LD LUD LL LW LW LL LLD 1.45E-03 6.53E-04 6.18E.05 4.012E05 2.20E-03 1.52-06 LWD 1.28E-05 8.95E-05 1.04E-04 LLD LLD LWD ULD LW UL LID L LD LD 1.3ME-02 7.65E-03 1.16E-03 2.16E-04 2.53E-02 LI LWD LUD LW LWD 1.47E-02 4.02E-03 6.20E-04 LWD 1.93E-02 762-02 3.82E-02 1.42E-02 2.91E-03 1.30E-01 LLD LWD LWD LW LD n 2.032-06 UD 1.67E-06 1.16E2-0 4.86E-08 2.762-05 LW 2.32E205 125E-04 1.76E-04 UD LW LWD LWD LD UD LW LW LLD ULD W LW W LWD u NONE I NONE' NONE NONE 2.26E-01 1.322E-01 I 3.76E-02 2.83E-02 4.24E-01 LLW LW LW LWD LWD

frbh.UD LL 4.50 LWD LWD 4.50E-03 iL L LD LD L LWD LLD eLL l rLD L L L LLD LWL LLD e NONE NONE NONE NONE NONE

. * r l i ND 4.50E-03 ND ND 4.502-3 LD = Below the Lower ULimt of Detectability, InuCrih (Table 4)

Form 12-ENVO1.O5F01 pe 11o 21).1 Ri I RTL.#A9.690E Beaver Valley Power Station - Units I & 2 Annual Radioactive Effluent Release Report Calendar Year - 200O Page 11 of 21 Table 283-C Uquld Efluents - Continuous Releases N/A NWA NWA NWA N/A NWA NWA HtA NWA N/A N/A W/A N/A NIA N/A NIA NMA WA tA N/A NfA NWA W/A W/A N/A NfA NIA WNA N/A NA WA NNA NfA N/A N/A N/IA NfA W/A N/A N/A A N/A NA N/A N/A N/A NfA N/A NA N/A N/A NWA N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A WNA N/A N/A N/A N/A N/A NIA N/A N/A N/A NWA N/A N/A N/A N/A NA N/A N/A N/A N/A N/A NA NI/A N/A N/A N/A N/A N/A N/A N/A NWA N/A N/A N/A NWA N/A NWA N/A WA N/A N/A NfA N/A N/A: N/A NA N/A N/A N/A N/A N/A WNA N/A N/A N/A NfA N/A N/A N/A N/A W/A N/A W/A N/A NA N/A WNA N/A N/A N/A NWA NWA N/A I

. NtA N I N/A : N/A l NIA I N/A

~t~o ~j ~ NIA N/A N/A N/A N/A F4 NIA NIA WNA N/A NIA kiNI Ji ; :rI R m N/A A NIA N/VA N/A N/A N/A N.A 4 .ke rn 3& ,i i X E . l N/A N/A N/A N/A N/A

~ _-i e Nt A A N/A N/ N/A 7N/ IIA

,_0 _

ero- _ NA l NA N/A 7 N/A TN/A N/A = Not Applicable (iqulds not discharged hI a continuous mode during this period)

Form 112-E-1.05.F01 (page 12 of 21), Rev I RTL#AS6E Beaver Valley Power Station - Units I & 2 Annual Radioactive Effluent Release Report Calendar Year - 2005 Page 12 of 21 Table 3A .

Solid Waste And Irradiated Fuel Shipments (Part I of 3)

MO1 mS t3 1 0.0% (1) -1 J 30.0%

i70

%4 1%

2%

¶4 1% %4

%4

¶4f

%6 I ¶4 i% I¶%

2 2 %4 I% i%

I% %4

¶% %4

% %4

¶%

i¶%

ff

%4

1 II ii a 4 o 0 1 2 0 0 o O O .

9 6

68 0 a 6 4 4 2 7 4

1. 2 1 .

O I 0 (1) Since container volumes are provided by the burial site, a calculational error of zero Is assumed.

(2) Percent values for any nuclide that are cO.01 % are not shown on this table. Data is available upon request

Fomn 112hENV-01.05.F01 (page 13 of 21). Rev I RIMMA9 Beaver Valley Power Station - Units I & 2 Annual Radioactive Effluent Release Report.,

CalendarYear -2005 Page 13 of 21 Table 39 Soid Waste And Irradiated Fuel Shipments (Part 2 of 3)

(1)Since container volumes are prvided by the burial site, a calculational error of zero Is assumed.

(2)Percent values for any nucride that are -0.01 %are not smwn on ths table. Data Isavallable upon request

Form 1/2-ENV-01 .o0FO1 (page 14 of 21), Rev I RTLF #A9.S9VE Beaver Valley Power Station - Units 1 & 2 Annual Radioactive Effluent Release Report Calendar Year - 2005 Page 14 of 21 Table 3C Solid Waste And Irradiated Fuel Shipments (Part 3 of 3)

O.OOE+00 m3 O.OOE+00 m3 O.GGE+DO m3 O.OOE'00 m3 j flnhl.

n flel a~I AflfF.fnl 1 (1) Since container volumes are provided by the burial site, a calculational error of zero Is assumed.

(2) Percent values for any nuclide that are <0.01 % are not shown on this table. Data Is available upon request.

Fomn 112-ENV-1.05.FO1 (page 15 of 21), Rev I RTL 6 A9.690E Beaver Valley Power Station - Units I & 2 Annual Radioactive Effluent Release Report alendar Year - 200S- Page 15 of 21 able 4 Lower LimIts Of Detectability (LID)

V .,I tic4-OR I -04 2.18E-13 1E-11 IE-04 5E82-07 V.71-131-1 50-E 12-04 t.2BE-4 tE-07 1.63-13 12-11

(.ooE-06 IE-06 4.944E8 - E-07 2T7E-13 1E-11 2*02-07 20 572E-14 1E-11 2.92-08 IE-04 1A9248 SE-07 2.46E-08 5E-07 1.69E-13 1E-11 GAOE-06 IE-04 1.71-Q8 5E-07 1.62E-13 1E-11 IU3M-O IE-04 1E-11 USE-41 6E-07 1S2E-13 2*02-0 IE-04 7.62E48 1tE05

&WE-481I-04

.1.89200 1E-05

1. a 3 1E-04 .08-08 1E-05 I.70527 1E-04 - 7RE-08 IE-05

&47E-08 82-08 (t)nE-5 5E-08 1J.0E-13 1E-11 I1.002-14 1E-11 1.2E-07 1E-04 .11E-08 5E-07 2.42E-13 1E-11 1.20-07 1E-04 3.E29-08 5E-07 1.22E-13 1E-11 8.02E-08 IE-04 *5SE08 6E-07 (.C0E-13 1E-11 1.42E-07 IE-04 3.60E-08 5E-07 1.42E-t3 IE-11 4.6E-08 IE-04 1.19E-08 SE-07 4.732E-14 E-11 4.17E-08 12.04 1.65E508 5E-07 4.61E-14 1E-11 4.?3E-t4 tE-tt 5.24E-08 IE-04 Z13E-08 5E-07 1.104-13 1E-11 1.10E-13 1E-11 2.X-E40 1E-04 9.46E-09 E-07 2*42-07 I2-04 7.122-08 5E-07 1.55E-13 1E-11 CIZE-08 IE-04 1.700 IE-06 1.082-I 1E-12 M.7E-0 - 1E-04 2=- SZE-0BE7 1.6SE-14 1E-10 t2.E-07 1E-04 G3E-08 SE-07 1.64E-13 1E-11 2.28E-06 IE-04 7.44E0 1E-05 1.2E-7 1E-04 S1JE-08 1E-05 4.772-07IE-04 14A-07 t-05 6.&E2-8 1E-04 1.602-08 1E-05 642-0E48 AE-04 2.24E-08 E0-05

.642-E07 1E-04 1*8E-07 1E-04 -61E4* 1E-05 2.62-08 1E-04 LS- - J E-07 -64 iE09 (1 211-1 1.54E-3 1-1 1E-11

.3-05 1E-04 2.38E-0 5E-07 1.5UE-13 1E-11 6.1Z-07 1E-04 2.762-13 12-11

.53E-07 1E-04 - 6.63E4 - E-07 1.282-13 1E-11 18E-07 1E-04 &34E-08 5E-07 1*5E-13 4121

.5208 1E-04 1S2E- GE-07 1.102-3 1E-11

&61E-07 IE-04 M~E407 6 E-07 1.35-12 12I-11 (1) 1.00E iE.07 (1)Sample analyses performed by a contractor laboratory.

(2)These LLD calculations contaIn a default weekly continuous sample volume of 2.85E*8 cc. Therefore, grab sample LID values reflectadifferentvolume (e 10cuftor2.83E+Scc).

431 The calculated UD%', except those denoted by (1), are from a counteridetector calibration on 11121105 These values are typical for other counterldetectors used for effluent counting at BYPS.

(4)Based on counting 60 ml of the water that was bubbled through a 20 liter aIr sample.

Forn 112-ENV-01.05.FO1 (page 16 of 21), Rev 1 FML # A9.690E Beaver Valley Power Station - Unit I Annual Radioactive Effluent Release Report calendar Year - 2005 Page 16 of 21 Table 6A Assessment Of Radiation Doses 7.13E-03 0.1426 2.882-03 0.0576 1.272-03 0.0254 2.91E203 0.0582 I.42E-02 0.1419 2.93E-02 0.5860 2.23E-02 0.4460 4.39E-03 0.0878 5.97E-03 0.1194 6.20E-02 0.6196 1.82E-02 12133 -1.81E-02 1.2067 3.39E-03 0.2260 4.12E-03 0.2747 4.38E-02 1A603 8.37E-03 0.1674 1.42A-02 0.2840 2.47E-03 0.0494 1.35E.03 0.0270 2.64E-02 0W2M39 2.172-02 0.4340 1.92E-02 0.3840 3&4E-03 0.0828 3.27E-03 0.0654 4.73E-02 0.4731 8.7E-03 0.1734 1.44E-02 0.2880 2.78E-03 0.0556 1.822-03 0.0364 2.77E-02 02767 2.S7E-02 0.5340 2.44E-02 0.4880 4.64E-03 0.0928 4.OE4-03 0.0800 5.97E-02 0.5974 t22 uo uggcr o acEo ooo ocoEWo ozw ogcl po 1222-09 0.0000 1.092E0 0.0000 0.002+00 0.0000 0.002400 0.0000 1.09E-06 0.0000 7.92-10 O 1.60I-01 0.0000 0.8400 0.002 0.0000 8.E02 0.000 47E-08 0.0500 0.002+00% 0.0000 0.002400 0.0000 0002+00 0.0000 0.002+00 0.0000 0.002+00 0.0000 1222-01 1.6267 1.3812-01 1.8400 9.94E-02 1.3253 8.3225-02 1.1093 4.43E-01 2.9507 1.22E-01 1.6267 1.382-01 1.8400 9.94E202 1.3253 8.322-02 1.1093 4.43E-01 2.9507 122E-01 1.6267 1.382-01 1.8400 9.94E-02 1.3253 8.32-02 1.1093 4.43E-01 2.9507 1.222-01 1.6267 1.38E-01 1.8400 9.942-02 1.3253 8.32E-02 1.1093 4.43E-01 2.9507 1.222-01 1.6287 1.3820 1.8400 9.942-02 1.3253 8.322-02 1.1093 4.43E-01 2.0507 1.222-01 1.6267 1.38-E01 1.8400 9.942-2 1.3253 8.322-02 1.1093 4.432-01 2.9507 (1) These doses are listed In mrem; they are calculated for the ma dmum indidual for all batch liquld effluents (2) These doses are hsted In nrad; they are calculated at the site boundary for batch &continuous gaseous effluents (0.4 males NW)

(3) These doses are fisted In mrem; they are calculated for the most likely exposed real individual (chIld) via all real pathways at 0.89 miles NW.

Umits used for calculation of percent (%) are from ODCM procedure 112-ODC-3.03, Attachment H Control 3.11.1.2, Attachment L Control 3.11.2.2, and Attachment M Control 3.11.2.3 (considered to be the design objectives).

ForM 1/2-ENV-1.05.FOI (page 17 of 21), Rev 1 RTL#A.690E Beaver Valley Power Station - Unit 2 Annual Radioactive Effluent Release Report Calendar Year - 2005 Page 17 of 21 Table 5B Assessment Of Radiation Doses

¶ ~

--, -A-4 3 7.13E-03 0.1426 2.88E-03 0.0576 127E-03 0.0264 2.91E-03 0.0582 1.42E-02 0.1419 2.93E-02 0.5860 2.23E-02 OA460 4.39E-03 0.0878 5.97E-03 0.1194 6.20E-02 0.6196 1.82E-02 1.2133 1.81E-02 12067 3.39E-03 0.2260 4.12E-03 02747 4.38E-02 1A603 8.37E-03 0.1674 1.42E-02 0.2840 2.47E-03 0.0494 1.35E-03 0.0270 2.64E-02 0.2639 2.17E-02 0.4340 1.92E-02 0.3840 3.14E-03 0.0628 327E-03 0.0654 4.73E-02 0.4731 8.67E-03 0.1734 1.44E-02 028801 2.78E-03 0.0556 1.82E-03 0.0364 2.77E-02 0.2767 2.67E-02 0.5340 2.44E-02 0.4880 I 4.64E-03 0.0928 4.OOE-03 0.0800 5.97E.02 0.5974

. .gW .i.fi -

ZM 0.000 2Z3E-05 0.0005 OJXE+00 0.0000 0..OOE+O 0.0000 2.53E-05 0.0003 7.09E-10 o.oo00 7.28E.5 0.0007 0=15E+00 0.0000O.OWE+O0 0.0000 7.26E-05 0.0004 O.0OE40 0.0000 1.74E.04 0.0023 O.OOE+00 0.0000 0.OOE+00 o.o000 1.74E-04 0.0012 5.833-03 0.0751 3.11E102 OA147 3.64El02 0.4720 8.97E-03 0.1196 8.11E-02 0.6407 6.63E.03 0.0751 3.1ED-02 0.4147 3.64E-02 0.4720 8.97E.03 0.1196 8.11E-02 0.5407

.ME-03 0.0751 3.11E-02 OA147 3S.4E.02 0.4720 8M97EM03 0.1196 8.11E-02 0.5407 56.3E-03 0.0751 3.IIE-02 0A147 3.54E32 0.4720 8.97E-03 0.1196 8.11E-02 0.5407 5.63E-03 0.0751 3.12E-02 OA160 3.54E102 0.4720 8.97E.03 0.1196 &12E-02 0.5413 5.63E-03 0.0751 3.11E-02 OA147 3.54E-02 0.4720 8.97E-03 0.1196 8.IIE-02 0.6407 (1) These doses are listed In mrem; they are calculated for the maximum Individual for aSl batch liquid effluents (2) These doses are listed In mrad; they are calculated at the site boundary for batch & continuous gaseous effluents (0.4 miles NW)

(3) These doses are listed In nerm; they are calculated for the most likely exposed real Individual (child) via all real pathways at 0.89 miles NW.

Umita used for calculation of percent (%) are from ODCM procedure 112-0DC1S.03, Attachment H Control 3.11.1.2, Attachment L Control 3.11.2.2, and Attachment M Control 3.11.2.3 (considered to be the design objectives).

Form 12-ENVW-1.05.FOI (page 18 of 21), Rev 1 RTL # A9.690E Beaver Valley Power Station - Units I & 2 Annual Radioactive Effluent Release Report Calendar Year - 2005 Page 18 of 21 Table 6 AJ Effluent Montoring Instrumentation Channels (as required by procedure 12-ODC-3.03 of the OffsIte Dose Calculation Manual) were returned to Operable Status within 30 days during fftis report period.

Form 112-ENV-01.05.FO1 (page 19 of 21), Rev I RTL #A9.69OE Beaver Valley Power Station - Units I & 2 Annual Radioactive Effluent Release Report Calendar Year - 2005 Page 19 of 21 TIble 7 T~tal Dose Commitments, Total Effective Dose Equivalents and Population Doses I si'-.,

Ite 1 Pjrrsuant to 10 CFR 20.1301(a)(1), the Total Effective Dose Equivalent from licensed operation to the maximum Individual during eport period, Is 385 mrom. This Isa summation of Direct Radiation Exposure (calculated by comparingthe maxnmum of al pirimeter lTD exposures to SLD exposure at the REMP control location) plus Effluent Doses (calculated per the ODCM).

E iiiff iiMitk.

9y t tr !ii ;i.-i

.. "1, __00mlfREMM 421 im radiation doses for IIEMBER(S) OF THE PUBUC due to their activities Inside the site boundaiy are not greater than the doses isted Inthis table to show compliance with 40 CFR Part 190 or10 CFR20.1301. Evaluations have shown thatexposure time for Individuals not occupationally associated with the plant ske Is minimal In comparison to the exposure time considered for the dose calculation at or beyond the ste boundary. Therefore, a separate assessment of radiation doses from radioactive effluents to MEIMER(S) OF THE PUBUC, due to their activities Inside the sHe boundary, Is not necessary for this report period.

0.60 mile Total Population Dose from liquid and gaseous effluents a 1238 man-mrem (Total Body) 0-60 mile Average Individual Dose from liquid and gaseous effluents a 0.0003096 mrem (Total Body)

Form 1/2ENV-01.05.Fol (page 20 of 21), Rev 1 RhL#AM.690E Beaver Valley Power Station - Units I & 2 Annual Radioactive Effluent Release Report Calendar Year - 2005 Page 20 of 21 Table 8

Forn 112-ENV-01.05.FO1 (page 21 of 21), Rev I RIL#A9.69E Beaver Valley Power Station - Units I & 2 Annual Radioactive Effluent Release Report Calendar Year - 2005 Page 21 of 21 Table 9

Beaver Valley Power Station - Units I & 2 Annual Radioactive Effluent Release Report Calendar Year - 2005 Attachment I JoInt Frequency Distribution Tables An annual summnary of hourly meteorological data, Inthe form of joint frequency distribution, is provided for the calendar year as specified inthe ODCM.

61... 14HIM11,11 Hourly meteorological data Is not provided for specific periods of Abnormal Gaseous Release during the calendar quarters (as indicated In Regulatory Guide 1.21), for the following reasons:

1) All Gaseous Releases for the calendar year were determined to be within design objectives.

where as, the ODCM Dose and Dose Rate I-imits are considered to be the design objectives,

2) There were no Abnormal Gaseous Releases during the calendar year.

For a copy of the hourly meteorological data during the calendar quarters, contact Mr. Anthony T. Lonnett at 724-682-7523.

Beaver Valley Power Station - Units I & 2 Annual Radioactive Effluent Release Report Calendar Year -2005 Attachment I Part 1: Joint Frequency Distribution Tables (35ft)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 1 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:11 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD 05010101-05123124 STABILITY CLASS: A DT/DZ ELEVATION: SPEED:SP 35P DIRECTION:DI 35P LAPSE:DT150-WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL N 14 32 1 0 0 0 47 NNE 19 16 0 0 0 0 35 NE 22 21 0 0 0 0 43 ENE 17 48 1 0 0 0 66 E 15 20 0 0 0 0 35 ESE 18 22 1 0 0 0 41 SE 17 12 0 0 0 0 29 SSE 7 16 0 0 0 0 23 S 7 19 0 0 0 0 26 SSW 9 49 0 0 0 0 58 SW 10 28 12 0 0 0 50 WSW 7 53 14 0 0 0 74 W 9 85 9 0 0 0 103 WNW 13 60 8 0 0 0 81 NW 18 35 6 0 0 0 59 NNW 16 35 2 0 0 0 53 TOTAL 218 551 54 0 0 0 823 PERIODS OF CALM(HOURS): 2 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 50 ENTER: [RETURN] CONTINUE, [SO] START OVER, [EX] TO EXIT

Beaver Valley Power Station-Ulits 1& 2 Annual Radioactive Effluent Release Report Calenda Year-205 Pat 1: Joint Frequency Distribution Tables (35fr)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 2 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:11 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD - 05010101-05123124 STABILITY CLASS: B DT/DZ ELEVATION: SPEED:SP 35P DIRECTION:DI 35P LAPSE:DT150-WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL N 6 6 0 0 0 0 12 NNE 8 16 0 0 0 0 14 NE 4 4 0 0 0 0 8 ENE 3 2 0 0 0 0 5 E 6 5 0 0 0 0 11 ESE 3 1 0 0 0 0 4 SE 3 0 0 0 0 0 3 SSE 3 1 0 0 0 0 4 S 1 5 0 0 0 0 6 SSW 0 11 1 0 0 0 12 SW 5 11 5 0 0 0 21 WSW 2 14 3 1 0 0 20 W 7 26 4 0 0 0 37 WNW 4 18 0 0 0 0 22 NW 5 7 2 0 0 0 14 NNW 6 8 0 0 0 0 14 TOTAL 66 125 15 1 0 0 207 PERIODS OF CALM(HOURS): 2 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 50 ENTER: [RETURN] CONTINUE, [SO] START OVER, [EX] TO EXIT

Beaver Valley Power Station - Units I& 2 Annual Radioactive Effluent Release Report Calendar Year - 2005 Part l: Joint Frequency Distibution Tables (35ft)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 3 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:11 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD = 05010101-05123124 STABILITY CLASS: C DT/DZ ELEVATION: SPEED:SP 35P DIRECTION:DI 35P LAPSE:DT150-WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL N 7 9 1 0 0 0 17 NNE 7 4 0 0 0 0 11 NE 11 4 0 0 0 0 15 ENE 5 3 0 0 0 0 8 E 5 1 0 0 0 0 6 ESE 1 0 0 0 0 0 1 SE 3 3 0 0 0 0 6 SSE 4 2 0 0 0 0 6 S 1 4 1 0 0 0 6 SSW 1 12 1 0 0 0 14 SW 2 16 7 0 0 0 25 WSW 3 20 6 0 0 0 29 W 7 23 11 0 0 0 41 WNW 7 16 3 0 0 0 26 NW 7 9 1 0 0 0 17 NNW 7 13 1 0 0 0 21 TOTAL 78 139 32 0 0 0 249 PERIODS OF CALM(HOURS): 2 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 50 ENTER: [RETURN] CONTINUE, [SO] START OVER, [EX] TO EXIT

Beaer Valley Power Station - Units 1 & 2 Annual Radioactive Effluent Release Report Calenda Year -2005 Attachment I Part 1: Joint Frequency Disribution Tables (35ft)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 4 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:11 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD 05010101-05123124 STABILITY CLASS: D DT/DZ ELEVATION: SPEED:SP 35P DIRECTION:DI 35P LAPSE:DT150-WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL N 83 97 0 0 0 0 180 NNE 99 31 0 0 0 0 130 NE 131 16 0 0 0 0 147 ENE 96 44 0 0 0 0 140 E 50 11 0 0 0 0 61 ESE 35 1 0 0 0 0 36 SE 39 1 0 0 0 0 40 SSE 29 21 0 0 0 0 50 S 29 31 1 0 0 0 61 SSW 47 66 12 1 0 0 126 SW 58 177 106 9 0 0 350 WSW 73 233 95 9 0 0 410 W 71 314 85 0 0 0 470 WNW 78 215 21 0 0 0 314 NW 95 212 14 0 0 0 321 NNW 92 -121 6 0 0 0 219 TOTAL 1105 1591 340 19 0 0 3055 PERIODS OF CALM(HOURS): 2 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 50 ENTER: [RETURN] CONTINUE, [SO] START OVER, [EX] TO EXIT

Beaver Valley Power Station-Units 1 &2 Annual Radioactive Effluent Release Report Calendar Year -2005 Attachment 1 Part 1: Joint Frequency Distribution Tables (35ft)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 5 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:11 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD 05010101-05123124 STABILITY CLASS: E DT/DZ ELEVATION: SPEED:SP 35P DIRECTION:DI 35P LAPSE:DT150-WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL N 90 14 0 0 0 0 104 NNE 104 4 0 0 0 0 108 NE 161 11 0 0 0 0 172 ENE 197 66 0 0 0 0 263 E 191 20 0 0 0 0 211 ESE 147 4 0 0 0 0 151 SE 138 3 0 0 0 0 141 SSE 95 14 0 0 0 0 109 S 158 29 4 0 0 0 191 SSW 139 79 12 0 0 0 230 SW 87 98 35 3 0 0 223 WSW 65 59 26 0 0 0 150 W 56 54 16 0 0 0 126 WNW 66 29 5 0 0 0 100 NW 77 45 1 0 0 0 123 NNW 74 22 1 0 0 0 97 TOTAL 1845 551 100 3 0 0 2499 PERIODS OF CALM(HOURS): 2 VARIABLE DIRECTION 0 -

HOURS OF MISSING DATA: 50 ENTER: [RETURN] CONTINUE, [SO] START OVER, (EX] TO EXIT

Beaver Valley Power Staon - Units I& 2 Annual Radioactive Effluent Release Report Calendar Yea- 2005 Atachment I 1 Part 1: Joint Frequency Distribution Tables (35ft)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 6 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:11 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD - 05010101-05123124 STABILITY CLASS: F DT/DZ ELEVATION: SPEED:SP 35P DIRECTION:DI 35P LAPSE:DT150-

_______________________________________WIND________EE___________

WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL N I 10 1 0 0 0 0 I11 NNE 15 2 0 0 0 0 17 NE 34 0 0 0 0 0 34 ENE 37 0 0 0 0 0 37 E 127 0 0 0 0 0 127 ESE 238 0 0 0 0 0 238 SE 260 0 0 0 0 0 261 SSE 194 2 0 0 0 0 197 S 120 4 0 0 0 0 124 SSW 58 15 0 0 0 0 73 SW 34 7 4 0 0 0 45 WSW 16 3 0 0 0 0 19 W 6 0 0 0 0 0 6 WNW 7 0 0 0 0 0 7 NW 18 0 0 0 0 0 18 NNW 7 1 0 0 0 0 8 TOTAL 1181 35 4 0 0 0 1222 PERIODS OF CALM(HOURS): 2 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 50 ENTER: [RETURN] CONTINUE, [SO] START OVER, [EX] TO EXIT

Beaver Valley Power Station-Units 1& 2 Annual Radioactive Effluent Release Report Calendar Year - 2005 Attachment 1 Part 1: Joint Frequency Distribution Tables (35ft)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 7 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:11 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD - 05010101-05123124 STABILITY CLASS: G DT/DZ ELEVATION: SPEED:SP 35P DIRECTION:DI 35P LAPSE:DT150-WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL N 5 2 0 0 0 0 7 NNE 9 2 0 0 0 0 11 NE 18 0 0 0 0 0 18 ENE 20 0 0 0 0 0 20 E 40 0 0 0 0 0 40 ESE 140 0 0 0 0 0 140 SE 167 0 0 0 0 0 167 SSE 108 0 0 0 0 0 108 S 62 3 0 0 0 0 65 SSW 27 2 0 0 0 0 29 SW 21 0 0 0 0 0 21 WSW 8 0 0 0 0 0 8 W 6 1 0 0 0 0 7 WNW 0 0 0 0 0 0 0 NW 9 0 0 0 0 0 9 NNW 5 0 0 0 0 0 5 TOTAL 645 10 0 0 0 0 655 PERIODS OF CALM(HOURS): 2 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 50 ENTER: [RETURN] CONTINUE, [SO] START OVER, [EX] TO EXIT

Bear Valley Power Statin - Units 1 & 2 Annual Radioactive Effluent Release Report Calendar Yer -2005 Attachment I Part 1: Joint Frequency Distributon Tables (35ff)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 8 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:11 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD - 05010101-05123124 -

STABILITY CLASS: ALL DT/DZ ELEVATION: SPEED:SP 35P DIRECTION:DI 35P LAPSE:DT150-WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL N 215 161 2 0 0 0 378 NNE 261 65 0 0 0 0 326 NE 381 56 0 0 0 0 437 ENE 375 163 1 0 0 0 539 E 434 57 0 0 0 0 491 ESE 582 28 1 0 0 0 611 SE 627 19 0 0 0 0 647 SSE 440 56 0 0 0 0 497 S 378 95 6 0 0 0 479 SSW 281 234 26 1 0 0 542 SW 217 337 169 12 0 0 735 WSW 174 382 144 10 0 0 710 W 162 503 125 0 0 0 790 WNW 175 338 37 0 0 0 550 NW 229 308 24 0 0 0 561 NNW 207 200 10 0 0 0 417 TOTAL 5138 3002 545 23 0 0 8710 PERIODS OF CALM(HOURS): 2 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 50 ENTER: [RETURN] CONTINUE, [SO] START OVER, (EX] TO EXIT

Beaver Valley Power Station - Units 1& 2 Annual Radioactive Effluent Release Report Calendr Year -2005 Attachment 1 Part 2: Joint Frequency Distribution Tables (150ft)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 1 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:12 HOURS ATEACH WIND SPEED AND DIRECTION PERIOD OF RECORD 05010101-05123124 STABILITY CLASS: A DT/DZ ELEVATION: SPEED:SP150P DIRECTION:DI150P LAPSE:DT150-WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL N 1 28 18 1 0 0 48 NNE 4 35 13 2 0 0 54 NE 0 17 11 0 0 0 28 ENE 0 23 36 5 0 0 64 E 0 35 16 2 0 0 53 ESE 1 27 11 0 0 0 39 SE 0 30 18 0 0 0 48 SSE 0 18 20 3 0 0 41 S 1 13 29 0 0 0 43 SSW 4 11 15 0 0 0 30 SW 1 15 9 3 0 0 28 WSW 2 17 19 6 0 0 44 W 0 42 58 15 1 0 116 WNW 6 29 49 26 1 0 111 NW 5 12 13 5 0 0 35 NNW 8 18 12. 2 1 0 41 TOTAL 33 370 347 70 3 0 823 PERIODS OF CALM(HOURS): 0 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 50 ENTER: [RETURN] CONTINUE, [SO] START OVER, [EX] TO EXIT

Beaver Valley Power Station - Units 1 & 2 Annual Radioactive Effluent Release Report Calendar Year- 200 Part 2: Joint Frequency Distribution Tables (I50ft)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 2 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:12 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD = 05010101-05123124 STABILITY CLASS: B DT/DZ ELEVATION: SPEED:SP150P DIRECTION:DI150P LAPSE:DT150-WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL

_____1 ___ 7__ 0__ 0___ 0-- 13---

N 1 7 5 0: 0 0 13 NNE 1 8 5 0 0 0 14 NE 2 5 1 0 0 0 8 ENE 0 3 1 0 0 0 4 E 1 10 4 0 0 0 15 ESE 0 4 2 0 0 0 6 SE 0 5 1 0 0 0 6 SSE 0 4 0 0 0 0 4 S 1 2 8 0 0 0 11 SSW 0 4 6 0 0 0 10 SW 2 2 6 0 0 0 10 WSW 3 3 7 2 0 0 15 W 1 20 9 6 1 0 37 WNW 0 16 12 3 0 0 31 NW 0 9 4 2 0 0 15 NNW 2 4 2 0 0 0 8 TOTAL 14 106 73 13 1 0 207 PERIODS OF CALM(HOURS): 0 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 50 ENTER: (RETURN] CONTINUE, [SO] START OVER, EX] TO EXIT

Beaver Valley Power Sttin - Uis1 & 2 Annual Radioactive Effluent Release Report Calendar Ya -2005 Atachment 1 Part 2: Joint Frequency Distribution Tables (150ft)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 3 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:12 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD = 05010101-05123124 STABILITY CLASS: C DT/DZ ELEVATION: SPEED:SP150P DIRECTION: DI150P LAPSE: DT150-WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL N 2 8 5 1 0 0 16 NNE 2 10 6 1 0 0 19 NE 1 6 1 0 0 0 8 ENE 0 11 4 0 0 0 15 E 0 4 4 0 0 0 8 ESE 0 3 0 0 0 0 3 SE 1 3 2 0 0 0 6 SSE 0 8 1 0 0 0 9 S 1 11 3 1 0 0 16 SSW 0 3 5 0 0 0 8 SW 1 6 5 1 0 0 13 WSW 3 7 10 4 0 0 24 W 4 10 17 16 1 0 48 WNW 3 8 11 11 0 0 33 NW 3 1 5 0 0 0 9 NNW 4 6 4 0 0 0 14 TOTAL 25 105 83 35 1 0 249 PERIODS OF CALM(HOURS): 0 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 50 ENTER: (RETURN] CONTINUE, (SO] START OVER, [EX] TO EXIT::

Beaver Valley Power Station - Units I & 2 Annual Radioactive Effluent Release Report Calendar Yer -2005 Attacbment I Part 2: Joint Frqacncy Distzibution Tables (IS0fft)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 4 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:12 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD = 05010101-05123124 STABILITY CLASS: D DT/DZ ELEVATION: SPEED: SP1SOP DIRECTION: DI150P LAPSE: DT150-WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 :->24-TOTAL N 33 93- 60 3 0 0 189 NNE 40 84 35 2 0 0 161 NE 27 59 7 0 0 0 93 ENE 20 100 43 2 0 0 165 E 11 42 18 0 0 0 71 ESE 10 25 6 0 0 0 41 SE 8 27 5 0 0 0 40 SSE 6 35 14 0 0 0 55 S 13 40 40 0 1 0 94 SSW 15 43 40 3 2 0 103 SW 16 45: 128 24 2 0 215 WSW 30 73 111 40 3 0 257 W 42 128 286 167 26 2 651 WNW 32 119 225 74 7 0 457 NW 35 123 100 9 0 0 267 NNW 41 107 45 3 0 0 196 TOTAL 379 1143 1163 327 41 2 3055 PERIODS OF CALM(HOURS): 0 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 50 ENTER: [RETURN] CONTINUE, (SO] START OVER, (EX] TO EXIT

Beaver Valley Power Statiazi-Units 1& 2 Annual Radioactive Effluent Release Report Calendar Yen -2005 Attachment I Part 2: Joint Frequency Distnbution Tables (lS0ft)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 5 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:12 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD = 05010101-05123124 STABILITY CLASS: E DT/DZ ELEVATION: SPEED:SP150P DIRECTION: DI150P LAPSE: DT150-WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL N 68 40 7 0 0 0 115 NNE 94 35 9 0 0 0 138 NE 121 78 4 0 0 0 203 ENE 104 191 108 5 0 0 408 E 54 73 22 0 0 0 149 ESE 35 38 14 0 0 0 87 SE 26 29 7 0 0 0 62 SSE 22 37 23 0 0 0 82 S 50 44 26 10 0 0 130 SSW 50 77 42 4 0 0 173 SW 56 74 83 9 0 0 222 WSW 61 57 32 20 1 0 171 W 35 79 55 28 3 0 200 WNW 24 93 56 19 1 0 193 NW 27 56 14 0 0 0 97 NNW 26 31 11 1 0 0 69 TOTAL 853 1032 513 96 5 0 2499 PERIODS OF CALM(HOURS): 0 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 50 ENTER: [RETURN] CONTINUE, [SO] START OVER, [EX] TO EXIT

Beaver Valley Power Station-Units I & 2 Annual Radioactive Effluent Release Report Caledar Year- 2005 Part 2: Joint Frequency Distibution Tables (150ft)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 6 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:12 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD - 05010101-05123124 STABILITY CLASS: F DT/DZ ELEVATION: SPEED:SP150P DIRECTION:DI150P LAPSE:DT150-WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL N 75 7 2 0 0 0 84 NNE 123 23 1 0 0 0 147 NE 153 64 0 0 0 0 217 ENE 66 47 9 0 0 0 122 E 36 10 0 0 0 0 46 ESE 19 5 0 0 0 0 24 SE 14 8 0 0 0 0 22 SSE 14 14 4 0 0 0 32 S 36 15 1 0 0 0 52 SSW 82 40 5 0 0 0 127 SW 95 53 12 1 0 0 161 WSW 41 31 1 0 0 0 73 W 19 12 4 0 0 0 35 WNW 16 14 0 0 0 0 30 NW 17 5 0 0 0 0 22 NNW 22 6 0 0 0 0 28 TOTAL 828 354 39 1 0 0 1222 PERIODS OF CALM(HOURS): 0 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 50 ENTER: [RETURN] CONTINUE, [SO] START OVER, [EX] TO EXIT

Beaver Valey Power Station - Units 1 & 2 Annual Radioactive Effluent Release Report Calendar Year - 2005 Attachment I Part 2: Joint Frequency Distribution Tables (150ft)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 7 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:12 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD - 05010101-05123124 STABILITY CLASS: G DT/DZ ELEVATION: SPEED:SP150P DIRECTION:DI150P LAPSE:DT150-WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL N 26 3 0 0 0 0 29 NNE 43 21 0 0 0 0 64 NE 61 29 0 0 0 0 90 ENE 35 24 2 0 0 0 61 E 7 15 0 0 0 0 22 ESE 16 7 0 0 0 0 23 SE 8 6 0 0 0 0 14 SSE 6 7 1 0 0 0 14 S 15 24 3 0 0 0 42 SSW 37 45 3 0 0 0 85 SW 59 35 3 0 0 0 97 WSW 19 12 2 0 0 0 33 W 16 7 1 0 0 0 24 WNW 16 5 0 0 0 0 21 NW 11 5 0 0 0 0 16 NNW 15 5 0 0 0 0 20 TOTAL 390 250 15 0 0 0 655 PERIODS OF CALM(HOURS): 0 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 50 ENTER: [RETURN] CONTINUE, (SO] START OVER, [EX] TO EXIT

Bea Valley Powe Stion - Units 1 & 2 Annual Radioactive Effluent Release Report Calendar Year - 2005 Atachment 1 Part 2: Joint Frequency Ditbuion Tables (150f)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 8 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:13 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD - 05010101-05123124 STABILITY CLASS: ALL DT/DZ ELEVATION: SPEED: SP150P DIRECTION: DI150P LAPSE: DT150-

_______________________________________WIND________E____________

WIND SPEED(MPH)-

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL N 206 186 97 5 0 0 494 NNE 307 216 69 5 0 0 597 NE 365 258 24 0 0 0 647 ENE 225 399 203 12 0 0 839 E 109 189 64 2 0 0 -364 ESE 81 109 33 0 0 0 223 SE 57 108 33 0 0 0 198 SSE 48 123 63 3 0 0 237 S 117 149 110 11 1 0 388 SSW 188 223 116 7 2 0 536 SW 230 230 246 38 2 0 746 WSW 159 200 182 72 4 0 617 W 117 298 430 232 32 2 1111 WNW 97 284 353 133 9 0 876 NW 98 211 136 16 0 0 461 NNW 118 177 74 6 1 0 376 TOTAL 2522 3360 2233 542 51 2 8710 PERIODS OF CALM(HOURS): 0 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 50 ENTER: [RETURN] CONTINUE, [SO] START OVER, [EX] TO EXIT

Beaver Valley Power Station - tnhit 1 & 2 Annual Radioactive Effluent Release Report Calendar Year -2005 Attachment I Part 3: Joint Frequency Distibution Tables (500 ft)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 1 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:14 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD 8 05010101-05123124 STABILITY CLASS: A DT/DZ ELEVATION: SPEED:SP500P DIRECTION:DI500P LAPSE:DT500-WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL N 0 0 0 1 0 0 1 NNE 0 0 1 0 0 0 1 NE 0 0 0 0 0 0 0 ENE 0 0 0 2 0 0 2 E 0 0 0 0 0 0 0 ESE 0 0 1 0 0 0 1 SE 0 0 0 1 0 0 1 SSE 0 0 0 0 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 1 0 0 0 1 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 TOTAL 0 0 - 3 4 0 0 7 PERIODS OF CALM(HOURS): 1 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 315 ENTER: [RETURN] CONTINUE, [SO] START OVER, [EX] TO EXIT

Beaver Valley Power Station - Uits I & 2 Annual Radioactive Effluent Release Report CalendarYea-2005 Attacbment 1 Part 3: Joint Frequency Distdibution Tables (500 ft)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 2 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:14 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD 05010101-05123124 STABILITY CLASS: B DT/DZ ELEVATION: .SPEED:SP500P DIRECTION:DI500P LAPSE:DT500-WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24. >24 TOTAL N 0 0 0 0 0 0 0 NNE 0 0 4 0 0 0 4 NE 0 1 2 3 0 0 6 ENE 0 1 6 7 0 0 14 E 0 1 3 2 0 0 6 ESE 0 4 8 1 0 0 13 SE 0 0 9 0 0 0 9 SSE 0 0 2 0 0 0 2 S 0 0 2 0 0 0 2 SSW 0 0 1 0 0 0 1 SW 0 0 0 0 0 0 0 WSW 0 0 1 0 0 0 1 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 1 0 1 NNW 0 1 0 0 0 0 1 TOTAL 0 8 38 13 1 0 60 PERIODS OF CALM(HOURS): 1 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 315 ENTER: [RETURN] CONTINUE, [SO] START OVER, [EX] TO EXIT

I. -

Beaver Valey Power Station -Units 1 & 2 Annual Radioactive Effluent Release Report Calendar Year- 2005 Attachment 1 Part 3: Joint Frequency Distribution Tables (500 ft)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 3 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:14 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD 05010101-05123124 STABILITY CLASS: C DT/DZ ELEVATION: SPEED:SP500P DIRECTION:DI500P LAPSE:DT500-WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL N 0 3 4 2 0 0 9 NNE 0 2 3 0 0 0 5 NE 0 3 8 1 0 0 12 ENE 0 4 8 1 0 0 13 E 0 4 4 2 0 0 10 ESE 0 6 6 0 0 0 12 SE 0 6 10 2 0 0 18 SSE 0 1 4 2 0 0 7 S 0 1 6 2 0 0 9 SSW 1 0 1 1 0 0 3 SW 0 0 0 0 0 0 0 WSW 1 0 0 0 0 0 1 W 0 3 0 2 0 0 5 WNW 0 0 1 1 1 0 3 NW 0 1 2 0 2 0 5 NNW 0 1 2 1 1 0 5 TOTAL 2 35 59 17 4 0 117 PERIODS OF CALM(HOURS): 1 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 315 ENTER: [RETURN] CONTINUE, [SO] START OVER, (EXI TO EXIT

Beaver Valley Power Station - Uni 1 & 2 Annual Radioactive Effluent Release Report Calenar Year -2005 Attachment I Part 3: Joint Frequency Distribution Tables (500 ft)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 4 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:14 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD = 05010101-05123124 STABILITY CLASS: D DT/DZ ELEVATION: SPEED: SP500P DIRECTION: DI500P LAPSE:DT500-WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL N 17 60 148 60 0 0 285 NNE 17 66 49 25 2 0 159 NE 27 78 26 5 0 0 136 ENE 21 63 106 48 5 0 243 E 20 81 103 40 2 0 246 ESE 19 47 85 20 2 0 173 SE 20 39 49 29 9 0 146 SSE 13 29 53 11 3 0 109 S 12 32 84 45 14 3 190 SSW 9 40 100 73 22 4 248 SW 18 54 120 188 56 8 444 WSW 27 60 128 148 30 5 398 W 18 96 236 307 151 32 840 WNW 13 75 257 270 60 19 694 NW 18 68 155 60 7 1 309 NNW 18 74 129 56 6 1 284 TOTAL 287 962 1828 1385 369 73 4904 PERIODS OF CALM(HOURS): 1 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 315 ENTER: [RETURN] CONTINUE, [SO] START OVER, [EX] TO EXIT

Beaver Valy Power Station - Units I & 2 Annual Radioactive Effluent Release Report CalenidarYcar-2005 Attachment 1 Part 3: Joint Frequmncy Distribution Tables (500 fi)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 5 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:14 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD = 05010101-05123124 STABILITY CLASS: E DT/DZ ELEVATION: SPEED: SP500P DIRECTION: DISOOP LAPSE:DT500-WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL N 18 15 23 12 0 0 68 NNE 28 21 9 8 0 0 66 NE 45 38 15 7 0 0 105 ENE 44 58 46 26 2 0 176 E 42 62 31 13 2 0 150 ESE 40 60 26 11 0 0 137 SE 31 55 33 21 3 0 143 SSE 24 36 19 19 2 0 100 S 25 21 39 46 14 0 145 SSW 41 22 26 38 9 0 136 SW 50 35 43 64 34 2 228 WSW 27 61 42 17 7 2 156 W 46 86 104 34 7 1 278 WNW 20 55 60 16 6 0 157 NW 32 23 24 11 0 0 90 NNW 23 16 19 5 0 0 64 TOTAL 536 664 559 348 86 5 2199 PERIODS OF CALM(HOURS): 1 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 315 X ENTER: [RETURN] CONTINUE, [SO] START OVER, [EX] TO EXIT

Beavw Valey Power Stton - Units I & 2 Annual Radioactive Effluent Release Report Calendar Year -2005 Attacbment I Part 3: Joint Frequency Distnibution Tables (500 ft)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 6 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:14 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD - 05010101-05123124 STABILITY CLASS: F DT/DZ ELEVATION: SPEED:SP500P DIRECTION:DI500P LAPSE:DT500-WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL N 11 17 6 3 0 0 37 NNE 14 7 2 0 0 0 23 NE 18 26 8 2 0 0 54 ENE 19 40 13 3 0 0 .75 E 21 53 10 0 - 0 0 84 ESE 31 37 7 3 0 0 78 SE 23 39 20 5 1 0 88 SSE 22 38 21 4 0 0 85 S 17 28 25 11 1 0 82 SSW 12 16 10 12 2 0 52 SW 26 33 25 22 8 1 115 WSW 29 23 5 0 0 0 57 W 32 23 17 8 0 0 80 WNW 16 29 15 0 0 0 60 NW 20 20 4 0 0 0 44 NNW 7 6 6 2 0 0 21 TOTAL 318 435 194 75 12 1 1035 PERIODS OF CALM(HOURS): 1 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 315 ENTER: [RETURN] CONTINUE, [SO] START OVER, [EX] TO EXIT

Beave Valley Por Station - lUits 1 & 2 Annual Radioactive Effluent Release Report Calendar Yar -2005 Attachment I Par 3: Joint Frequency Distnribuon Tables (500 ft)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 7 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:14 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD - 05010101-05123124 STABILITY CLASS: G DT/DZ ELEVATION: SPEED:SP500P DIRECTION: DI500P LAPSE: DT500-WIND SPEED(MPH)

WIND

DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL

___ _____ _____ 0__ 1----

N 0 1 0 0 1 0 0 NNE 1 0 0 0 1 0 0 NE 0 1 0 0 1 0 0 ENE 0 1 0 0 1 0 0 E 1 4 0 0 5 0

ESE 3 6 1 0 0 10 0

SE 2 7 7 2 0 18 0

SSE 2 8 5 0 0 15 0

S 2 4 6 3 0 15 SSW 1 3 7 11 1 0 23 SW 1 12 4 6 0 0 23 WSW 1 5 0 0 0 0 6 W 1 1 0 0 0 0 2 WNW 0 1 0 - 0 0 0 1 NW 0 0 0 0 0 0 0 NNW 1 0 0 0 0 0 1 TOTAL 16 54 30 22 1 0 123 PERIODS OF CALM(HOURS): 1 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 315 ENTER: [RETURN] CONTINUE, [SO] START OVER, [EX] TO EXIT

Beaver Valley Power Station - Units I & 2 Annual Radioactive Effluent Release Report Calendar Yea -2005 Attachment I Part 3: Joint Frequency Distnbution Tables (500 ft)

OPROGRAM: MIDJF VERSION: 5.5 PAGE 8 OF 8 SITE: BEAVER VALLEY UNIT: ONE 02/23/06 11:14 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD - 05010101-05123124 STABILITY CLASS: ALL DT/DZ ELEVATION: SPEED:SP500P DIRECTION:DI500P LAPSE:DT500-WIND SPEED(MPH)

WIND DIRECTION 1-3 4-7 8-12 13-18 19-24 >24 TOTAL N 46 96 181 78 0 0 401 NNE 60 96 68 33 2 0 259 NE 90 147 59 18 0 0 314 ENE 84 167 179 87 7 0 524 E 84 205 151 57 4 0 501 ESE 93 160 134 35 2 0 424 SE 76 146 128 60 13 0 423 SSE 61 112 104 36 5 0 318 S 56 86 162 107 29 3 443 SSW 64 81 146 135 34 4 464 SW 95 134 192 280 98 11 810 WSW 85 149 176 165 37 7 619 W 97 209 357 351 158 33 1205 WNW 49 160 333 287 67 19 915 NW 70 112 185 71 10 1 449 NNW 49 98 156 64 7 1 376 TOTAL 1159 2158 2711 1864 473 79 8445 PERIODS OF CALM(HOURS): 1 VARIABLE DIRECTION 0 HOURS OF MISSING DATA: 315 ENTER: {RETURN] CONTINUE, [SO] START OVER, [EX] TO EXIT

RTL A9.690E Annual Radiological Environmental Operating Report (Annual REMP Report)

FirstEnergy Nuclear Operating Company FENOC Beaver Valley Power Station - Units I & 2 Unit I License No. DPR-66 Unit 2 Ucense No. NPF-73 Annual Radiological Environmental Operating Report Calendar Year - 2005

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report EECUTIVE

SUMMARY

This document provides a detailed report of the Beaver Valley Power Station (BVPS)

Radiological Environmental Monitoring Program (REMP). During te report period, samples of air, water, shoreline sediment, milk, fish, food crops, feed crops, vegetation, and direct radiation (in the vicinity of the BVPS site) have been measured, analyzed, evaluated, and summarized.

The results of the REMP are intended to verify that BVPS effluent releases, performed in accordance with the BVPS Radiological Effluent Technical Specification (RETS) program, do not impact the environment with measurable concentation of radioactive materials and/or levels of radiation that are higher than expected.

Pre-operational REMP (1974 -1975):

A pre-operational REMP program was performed during the period 1974 through 1975. At that time, samples were collected and analyzed to deternine the amount of radioactivity present in the enVironment prior to BVPS operation. The resulting values are considered a "baseline" to which current sample analyses can be compared. A summary of the preoperational data is summarizd in Table 2-3 of this report.

Operational REMP (1976 - Present):

The operational REMP program was initiated during calendar year 1976 and continued through the report period. During the past thirty (30) years, radiation and radioactivity in the environment was monitored within a 10-mile radius of the site. A description of the operational REMP program is outlined in Table 2-1 of this report. In general, two (2) types of samples were collected during the report period, and are described as follows:

Control Samules: These samples are collected from areas that are beyond measurable influence of BVPS operation, and are used as reference data. Normal background radiation levels, or radiation present due to causes other than BVPS operation, can thus be compared to the environment surrounding the BVPS -site. During the report period, tree-hundred-fifty-six (356) analyses were performed on samples from the control locations. In addition, eight (8) analyses were completed for TLD's at the control location. Results of the analyses from the control locations are summarized in Table 2-2 of this report

Indicator Samples: Indicator samples are collected to determine the radiological impact of BVPS operation in the environment These samples are collected from various locations near the BVPS site. At a minimum, the samples are collected from areas where the BVPS contribution would indicate the most significant radiological impact During the report period, one-thousand-five-umdred-nnet-four (1594) analyses were performed on samples collected from more than ninety (90) indicator locations. In addition, four-hundred-ninety-two (492) analyses were completed for TLD's at the indicator locations. Results of the analyses from the indicator locations are also summarized in Table 2-2 of this report Current analysis results from the indicator samples are compared to both current control sample values and the pre-operational baseline to determine if changes in radioactivity levels are attributable to station operations.

ii

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Special Renort Requirements:

A Special Report shall be submitted to the Nuclear Regulatory Commission when the level of radioactivity in an environmental sampling medium exceeds the limits specified in Offsite Dose Calculation Manual (ODCM) procedure 1/2-ODC-3.03, Attachment Q Table 3.12-2.

A Special Report shall also be submitted when the results of the following calculation are >1.0.

This calculation is performed when more than one radionuclide is detected in the sampling medium:

Concentration (1) + Concentration (2) + ... > 1.0 Limit Level (1) Limit Level (2)

Summary:

Based on the analytical results of environmental samples, the reporting levels were not exceeded during the report period.

Positive results attributable to the BVPS operation were consistent with station data of authorized radioactive discharges and were within limits permitted by the NRC license and the ODCM. Other radioactivity detected was attributable to naturally occurring radionuclides, previous nuclear weapons tests, other man-made sources, and to the normal statistical fluctuation for activities near the Lower Limit of Detection (LLD).

During the report period, the radioactive effluent releases from the BVPS site did not exceed the limits identified in the BVPS Operating License Technical Specifications, and/or the ODCM.

The National Academy of Sciences 1990 BEIR Report shows that the typical dose to an individual from background (natural radiation exposure including radon) is an estimated average of 296 mrem per year. During the report period, the average individual population dose (for 4 million people) from BVPS operation was much less than <1 mrenL Therefore, the average individual population dose was not affected from BVPS operation.

Analytical results are divided into the following exposure pathways:

Airborne Exposure Pathway: The airborne exposure pathway includes airborne radioiodine and airborne particulates. The results during this report period were similar to previous years. There was no notable increase in natural products and no detectable fission products or other radionuclides in the airborne particulate media during the year.

Direct Emosure Pathway: This pathway measures environmental radiation doses by use of Thermo-Luminescent Dosimeters (TLDs). The results of TLD processing have indicated a stable trend and compare well with previous years.

Ingestion Exposure Pathway: This pathway includes milk, fish, and food products (leafy vegetable) samples.

iii

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report For milk samples, Strontium-90 (attributable to past atmospheric weapons testing, was detected at levels similar to the past five years). The gamma spectrometry analyses only indicated positive results for naturally occurring Potassium-40 at average environmental levels. No other radionuclides were identified.

The fish samples indicated below LLD levels in each of the sample analyses.

Vegetation samples indicated naturally occurring Potassium40 at average environmental levels.

Waterborne Exposure Pathway: This pathway includes driking water, ground (well) water, surface (river) water, and river sediment.

Water samples were analyzed for tritium and gamia-emitting radionuclides. Tritium was identified in some of the water samples, but the values were consistent with tritium at the control location. Gamma spectrometry analysis of water samples indicated no radionuclides above detection capabilities. Iodine-131 analysis showed several positive analyses, but the values were consistent with Iodine-131 at the upstream control location.

Sediment samples were collected from upstream of the site, at the discharge point of BVPS liquid effluent releases, and downstream of the site. Analysis of samples indicated naturally occurring radionuclides Potassium-40, Thallium-208, Bismuth-214, Lead-210, Lead-214, Radium-226, and Actinimn-228 in all results. The analyses also indicated Cesium-137, but the values were consistent with Cesium-137 at the control location. The Cesium-137 is most likely due from previous nuclear weapons tests. Cobalt-58 and Cobalt-60 were identified in some of the samples that were obtained at the shore line of the main outfall facility. This is not unusual, because the BVPS site discharges Cobalt-58 and Cobalt-60 in liquid waste effluents. However, the activity detected at this sample location is consistent with discharge data of authorized liquid effluent releases. All liquid effluent releases during the report period did not exceed the release concentration limits set forth in the ODCM.

Other Exuosure Pathways: In addition to the required samples collected from the above exposure pathways, precipitation, and feed crops were also collected. Results were consistent with previous years and no degrading trends were identified.

The BVPS operational REMP program was followed throughout the report period. The results demonstrate the adequacy of radioactive effluent control at the BVPS, and that plant operation did not adversely affect the surrounding environment.

It should be noted that the REMprogram includes sampling sites in addition to the required sites set forth in the ODCM. These include five (5) air sampling sites, one (1) surface water site, three (3) ground water sites, three (3) precipitation sites, two (2) sediment sites, one (1) local large dairy, and one (1) milk animal feed site.

iv

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report I ECrl[E SlU~lM[M[ARY .............................. .... seem SECTION 1 -INTRODUCTION A. Scope and Objectives of the Program .............. 11 ......... -

B. Description of the Beaver Valley Site ............................ l-1 SECTION 2 - ENVIRONMENTAL MONITORING PROGRAM AL. Environmental Radioactivity Monitoring Program ........... ..... .. .......... 2-1

1. ProgpramlD escripdion ... ... 2-1

2. Sumnary of Results .......................... ................... 2-5

3. Qulality Control Irogram ~o.**.00.*e~e~ooeoe0.*o..*. 2-5

4. I0r00r mk6rge2-5 B. Air Monitoring 2-22

1. Characterization of Air and Meteorology o

.... ......... o...... omy.

.. 2-22

2. Air Sampling Program and Analytical Techniques nu ....... e 2-22

3. Results and Conclusions .................................... 2-23 C. Monitoring of Sediments and Soil ........................................ 2-26

1. Characterization of Stream Sediments and Soils ................... 2-26

2. Sampling Progranm and Analytical Techniques 2-26

3. Results and Conclusions ...... on........ .. O.................... 2-27 D. Monitoring of Feedcrops and Food Products ...... .. ......... messes..... ....... 2-31

1. Characterization of Farmi Products ... oo.s.o.....e..oo...o... ...... **me... 2-31

2. Sampling Program and Analytical Techniques ...................... 2-31

3. Results and Conclusions .................................................... 2-33 E. Monitoring of Local Cow and Goat Milk ......................................... 2-36

1. Description - Mdich Animal Locations .. ..... &oo.e......... s... 2-36

2. Sampling Program and Analytical Techniques ........................... 2-36

3. Results and Conclusions . ..............es.....ee.*e..s..e .... 2-38 F. Environmental Radiation Monitoring ............... 2-41

1. Description of Regional Background Radiation and Sources ..... .... 241

2. Locations and Analytical Techniques ... ..a......... . me....... 2-41

3. Results and Conclusions 2 ................... m............ 2-41 G. Moneitorizng of Fish. ... 00*00ele .. s 2-'S5

1. D escrd~ipto ..... 2o..... 4........ .*e . 2-5

2. Sampling Program and Analytical Techniques .......................... 2-45

3. Results and Conclusions ... 5...............................e.o9.eeo..ee 245 v

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report TABLE OF CONTENTS (Continued)

SECTION 2 - ENVIRONMENTAL MONITORING PROGRAM (continued)

H. Monitoring of Surface, Drinking, Ground Waters and Precipitation .............. o 2-48

1. Description of Water Sources ........ ..... ...... ......... *........... 2-48

2. Sampling and Analytical Techniques * * *........................... ........ 2-48

3. Results anid Conclusions ...... *..... o-o...... *.*a ........ ***.........**.**. 2-50 I. Estimates of Radiation Dose to Mvan ............. 2-57

1. Pathways to Man - Calculational Models ...................... ........... 2-57

2. Results of Calculated Population Dose to Man-Liquid Releases .... 2-57

3. Results of Calculated Population Dose to Man - Atmospheric Releases ..................................... .. 2-57

4. Conclutsio ns ........................

s. 2-58 SECIION 3 -LAND USE CENSUS .................. ............ 3-1 SECTION 4 -SPLiT SAMPLE AND SPIE SAMPLE, INER=-LABORATORY COM[PARISON PROGRAM ............... 4-1 A. Split Sample Program (Inter-Laboratory Comparison, Part 1 of 2) ............. 4-1 B. Spike Sample Program O(ter-Laboratory Comparison, Part 2 of 2) ........... 4-1 C. Conclusions ......... o.................................................... 4-3 vi

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report LIST OF TABLES Table 2-1, Operational Radiological Environmental Monitoring Program .... .................... 2-2 Table 2-2, Enviroimnental Mvonitoring Program Results ....... .. ......... ........................... 2-6 Table 2-3, Pre-Operational Environmental Radiological Monitoring Program Summary ..... 2-19 Table 2-4, Comparison of Natural Background Exposure Versus Calculated Population Dose to Mazn- Liquid Effluent Releases ................................................ 2-59 Table 2-5, Comparison of Natural Background Exosure Versus Calculated Population Dose to MIan - G(aseous Effluent Releases ................... .............. 2-6 Table 3-1, Location of Nearest Residents, Gardens, Dairy Cows, Doe Goats and Beef Cattle . 3-3 Table 4-1, Inter-Laboratory Comparison Program, Spiked Samples - li Quarter 4-4

..........o.'.o..

Table 4-2, Inter-Laboratory Comparison Program, Spiked Samples -2nd Quarter ........ ...... 4-5 Table 4-3, Inter-Laboratory Comparison Program, Spiked Samples - 3rd Quarter ................ 4-6 Table 4-4, Inter-Laboratory Comparison Program, Spiked Samples - 4h Quarter ............ .. 4-7 vil

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report LIST OF FIGURES Figure 1-1, Geographical Map and Principal Communities in 50-mile Radius of the Beaver Valley Power Station ............................................................. 1-3 Figure 2-1,]Environmental Monitoring Locations - Air Sampling Stations ...................... 2-24 Figure 2-2, Graph of Annual Average Concentration: Gross Beta in Air Particulates ......... 2-25 Figure 2-3, Environmental Monitoring Locations - Shoreline Sediments and Soil ............. 2-28 Figure 2-4, Graph ofAnnual Average Concentration: Cesium-137, Cobalt-58 & 60 In Sediment ........................................................................... 2-29 Figure 2-5, Graph of Annual Average Concentration: Cesium-137 in Soil ....................... 2-30 Figure 2-6, Environmental Monitoring Locations - Feed Crop and Food Product ............. 2-34 Figure 2-7, Graph of Annual Average Concentration: Cesium-137 in Feed and Food ......... 2-35 Figure 2-8, Environmental Monitoring Locations - Milk .. ......................................... 2-39 Figure 2-9, Graph of Annual Average Concentration: Iodine-131 in Milk ........... .............. 2-40 Figure 2-10, Environmental Monitoring Locations - TLIDs .... ......................... 2-42 Figure 2-11, Graph of Annual Average Exposure: Direct Radiation in Environment ........... 2-44 Figure 2-12, Environnental Monitoring Locations - Fish ........................................... 2-46 Figure 2-13, GraphofAnnual Average Concentration: Cesium-137 in Fish ..................... 2-47 Figure 2-14, Environmental Monitoring Locations - Ground Water, Surfice Water, Drinking Water and Precipitation ................. 2-52 Figure 2-15, Graph of Annual Average Concentration: Iodine-131 in Surface Water, and Drinking Water .aeCnetain.ii.nSufc.er....... 2-53 Figure 2-16, Graph of Annual Average Concentration: Tritium in Suroic Water ............. 2-54 Figure 2-17, Graph of Annual Average Concentration: Tritium in Ground Water ............. 2-55 Figure 2-18, Graph of Annual Average Concentration: Tritium in Drinking Water ....... 2-56 viii

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report SECT[ON 1- INTRODUCUION A. Scope and Objectives of the Program The enviromental program consists of environmental monitoring for radioactivity in the vicinity f the Beaver Valley Power Station. Environmental sampling and analyses included air, water, milk, vegetation, river sediments, fish, and ambient radiation levels in areas surrounding the site. The results of these media are assessed to determine impacts of the plant operation on the environment.

The Annual Radiological Environmental Report for the Beaver Valley Power Station summarizes the radiological enviental monitoring program conducted by the FirstEnergy Nuclear Operating Company during the report period.

B. Description of the Beaver Valley Site The Beaver Valley Power Station is located on the south bank of the Ohio River in the Borough of Shippingport, Beaver County, Pennsylvania, on a 501 acre tract of land. The site is approximately one mile from Midland, Pennsylvania; five miles from East Liverpool, Ohio; and twentyfive miles from Pittsburgh, Pennsylvania. Figure 1-1 shows the site location in relation to the principal population centers. Population density in the immediate vicinity of the site is relatively low. The population within a five mile radius of the plant is approximately 15,493 and the only area within the radius of concentrated population is the Borough of Midland, Pennsylvania, with a population of approximately 3,321.

The site lies in a valley along the Ohio River. It extends from the river (elevation 665 feet above sea level) to a ridge along the border south of the Beaver Valley Power Station at an elevation of 1,078 feet Plant grade level is approximately 735 feet above sea level.

The Beaver Valley Power Station is on the Ohio River at river mile 34.8, at a location on the New Cumberland Pool that is 3.3 river miles downstream from Montgomery Lock and Dam, and 19A miles upstream from New Cumberland Lock and Dam. The PennsylvaniaOhio-West Virginia border is located 5.2 river miles downstream from the site. The river flow is regulated by a series of dams and reservoirs on the Beaver, Allegheny, Monongahela and Ohio Rivers and their tributaries.

During the report period, the flow ranged from 7,900 cubic feet per second (minimum monthly average) to 131,400 cubic feet per second (maximum monthly average). The mean flow during the report period was 41,142 cubic feet per second).

Water temperature of the Ohio River typically varies from 340 Fahrenheit to 75C Fahrenheit. The minimum temperatures occur in January and/or February and maximum temperatures in July and'or August. Water quality in the Ohio River at the site location is affected primarily by the water quality of the Allegheny, Monongahela and Beaver rivers.

The climate of the area may be classified as humid continental. Total annual precipitation during the report period was 53.02 inches. Yearly temperatures varied from a low of 1.90 Fahrenheit to a high of 87.60 Fahrenheit with an annual average temperature of 51.20 Fahrenheit. The predominant wind direction is typically from the southwest in summer and from the west southwest in winter.

1-1

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report The basic features of the Beaver Valley Power Station Units 1 and 2 are tabulated below:

Beaver Valley Unit 1 Beaver Valley Unit 2 Licensed Power Level 2685 - megawatts thermal 2685 - megawatts thermal Type of Power PWR PWR No. of Reactor Coolant Loops 3 3 No. of Steam Generators &Type 3 - Vertical 3 -Vertical Steam Used by Main Turbine Satrated Saturated The units utilize two separate systems (primary and secondary) for transferring heat from the source (the reactor) to the receiving component (turbine-generator). Because the two systems are isolated from each other, primary and secondary waters do not mix; therefore, radioactivity in the primary system water is normally isolated from the secondary system. Reactor coolant in the primary system is pumped through the reactor core and steam generators by means of reactor coolant pumps.

Heat is given up from the primary system to the secondary system in the steam generators, where steam is formed and delivered to the main unit turbine, which drives the electrical generator. The steam is condensed after passing through the turbine, and returned to the steam generators to begin another steam/water cycle.

1-2

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Figure 1-1 Geographical Map and Principal Communities In 50-mile Radius of the Beaver Valley Power Station

=1-I M

0 -2 40 MUIES 1-3

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report SECTION 2 - ENVIRONMENTAL MONITORING PROGRAM A. Environmental Radioactivity Monitoring Program

1. Program Description The program consists of monitoring water, air, soil, river bottoms, vegetation and food crops, cows milk, ambient radiation levels in areas surrounding the site, and aquatic life as summarized in Table 2-1. Further description of each portion of the program (Sampling Methods, Sample Analysis, Discussion and Results) are included in Sections 2-B through 2-I of this report 2-B - Air Monitoring 2-C - Monitoring of Sediments and Soils 2-D - Monitoring of Feed Crops and Food Products 2-E - Monitoring of Local Cow and Goat Milk 2-F - Environmental Radiation Monitoring 2-G - Monitoring of Fish 2-H - Monitoring of Surface Water, Drinking Water, Ground Water and Precipitation 2-I - Estimates of Radiation Dose to Man 2-1

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Table 2-1 Operational Radiological Environmental Monitoring Program SectIon Se _ a Sample_________________

Sample Point Descpon Sample Frequency Sample Frequency I AnalysisPreparation _____

13 Hookstown PA (Old Meyer Fam) Corib keidy - . Grss Bela Parucuate & 27 Alquippa, PA uon Far Sampling with Particulate lb)

Radbonuclde 28 Sherman Farm Sampb 29B Beaver, Pa (Fdendship Ridge) Collection at bast Weekly -Charcoal oine-131 30 Shlppn t PA (Cook's Fenry Subsltation) weefy 32 Midland, PA (North Substation) Quarteriy Composite Gamma Scan 45.1 hldustry. PA idseeeN Service - RN 8) (c) 47 East ULerpool, OH W~ater Department) 48 Werton, WV (Water Tower-CollierWay) i i

51 Alicquppa, PA (Sheeld Substation) 10 Shippingport PA (Post Office) 2 1S Hookstown, PA (Old Meyer Farm Continuous MD) Quarterly () Gamma Dose Radlation 14 Hookstown. PA 16 Georgelown. PA (Post Office) 27 Aliqlppa. PA (Bnarnon Fami) 28 Sheman Farm 29B Beaver, PA (Frendship Ridge) 30 Shlpplngport, PA (Cookns Ferry Substation) 32 Midland, PA (North Substation) 3344 BVPS Site PerimeterLocations 45 Raccoon Township PA (Christian House BaptistChape RL 18) 45.1 Raccoon TAwnship, PA (Knneds Come, 48 Industry PA DMidway De 46.1 Industry, PA QkKeel8 Serice - Rit 68) 47 East Liverpool, OH Water Department) 48 Webirton, WV (Water Tower - Collier Way) 51 Aliquippa, PA (Shefflield Substation) 52-55 BVPS Site Perimeter Locations 59 236 Green HID Road e0 Georgetown, PA (444 HMliRoad) 70 hstustry, PA P38 Engle Road) 71 Srighton Township, PA (Frst esterm Bank) 72 Ohloview, PA Pithem Church - Rear) 73 618 Squirre Rum Road 74 Monaca. PA (37 PoplarAvenue - CC8C) 75 Alkqulppa, PA (117 Holt Road) 78 Raccoon Township. PA (Elementary SchooD 77 Allquippa, PA (3614 Green Garden Road) 78 Raccoon Township, PA (Municpal BuDdin 79 108N Ri151 -Ted MdWliWamsAuto Body 80 Raccoon Township, PA (Parc Office -RI 18) 81 Millcreek United Presby, Church 82 2897 RL 18 83 735 MID Creek Road 84 Hancock County, W (Senlor Center) 85 2048 R. 30 88 East Liverpool, OH (1090 Ohdo Avenue) 87 50103 Calcutta Smith's Feny Road 88 Mdland, PA (110 Summlt Road) 89 Oiloyllie. PA (488 SmIth Fe"y Road) 900 Midland, PA O82 Tuscarawmus Road) 91 Pine Gmve Road & Doyle Road Georgeton. PA (Georgetawn Road 92 Substation) 93 104 LInden - Sunrise Hills 94 Hookstlwn, PA (832 McCLeary Road)

Hooktown, PA (McCleary & Pole Cat Hollow 95 Roads) 111-112 BVPS Site Perdmeter Locations 2-2

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Table 2-1 Operational Radiological Environmental Monitoring Program Section SaTe of Sa Sam Point Description Sample Frequency s iaePepar A s Weeldy Grab S Surface 49 (a) Indusby, PA (Upstream of Montorneiy Sanmple (h) Wely Sample m Water Darn) Site4 only lodines-S1 Weekly Intermitent 2.1 M ,PAnL m)Sam Composite Sample Monthly Composite of Gamma Scan Daffy Grab Sample 5 East Liverpool, OH Water Department) Collected Weekly Quarterly Composite (C)

- -) - :_ - h ._ Titium S)

II Shlpplngiport, PA (Upstrearn) Gamma Scan 4 Groundwater 14a Hostwon, PA wnsream) Sernl SemiAnnual Tritium (H-3) 1-b Georgeown, PA (Downstream) 6 Drinking 4 Midland, PA Water Department) Weekly Composite of Water 6 East Liverpool, OH ffifater Department Intermittent (d) Daly sample (d) lodlne-S1 Sample Collected U Composite (d) Gamma Scan Weeklyt Quarterly Composite (d) Ttilurn (H 2A BVPS Outfall Vicinity S 49a br) y, PA (Upstream of Montgomery Semirnnual Semi-Anual Gamma Scan Sediment 49 Dam) so New Dam)Cumberlard, YIV (Upstream of _

7 UMlk Weekly (e) Weekdy Samples kmm Weekly 25 Hookstown, PA (Searight Farm) Searght only lodxIne-11 1mm Searight

_ _ _ __ __ _ _ _ _only 27 () Aliquippa, PA (rnton Farm)=

89 (Ic) Aliquippa, PA (Collins Farm) Biweky ( Wm Al other samples & Gamma- Scan 0 (a) B e PA ndahelmeriFammals are on analyses ae Biweekly lodne-1S1 98a Bgtttwn A IndhlmrFam ps mMonthly at during grazing, but 113 0 Hookstown, PA (Iaistead Farm) oertimes Monthly duringother Stontgu 11400 Hookstown, PA Moore Farm) 2A 8VPS Outfall Vicinity Gamra Scan a Fihh 49a Industry, PA (Upstream of Montgomery Sennual Composite of edble an edible Dam) - parts by species (g) parts 10a Shlppn t PA Gamma Scan 9 Food t5a Georgetown. PA Annual at Harvest Composite of each lodine-1S1 on P s 48a Industry, PA wnple specis samlbb green Iay 48a Werton vegetables

- -W W -on 10 6 25 Hookstown, PA (Searight Farm) Montml Monthly Gamma Scan Forage -

13 Ho ow PA (ad Meyer Farm) 11 Soi 22 South of BVPS, Transmisslon Unes Every Thee( ) 12 Core Samples 3" Gamma Scan 27 AMqIppa4 PA (Brunton Farm) Years Deep (2"dIameter at

. . .27 Beave, PA( aMiFarm) (1997, 2000, 2003) each location appro 10' 2SA Beaver, PA Ofa Farm) radius) 3Sa Shlplgort, PA (Cooks Feny Substation) 32a MAIdland, PA (oth Substation) 46b Industry, PA WIlows Inn - RL 68) 47a East Liverpool, OH Water Department) 4U Welrton WV (Water Tower - East Bellevlew Drive) 51a AluilpPa PA (Sheff eld Substation) r t ShIppingport PA (Cook's Ferry Weekly grab 12 PreSpitaion Substation) samples when Quarterly Composite (C) Ganua Scan 47 East Liverpool, OH Water Department) avaiable Td~un (H-3) 48 Weirton WV Water Tower-Collier Wa) 2-3

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Table 2-1 Operational Radiological Environmental Monitoring Program Notes for Table 2-1 (a) Control Sample Station: These Locations which are presumed to be outside the influence of plant effluents.

Particulate Samples are not counted within 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months after filter change. Perform Gamma (b) Isotopic analysis on each sample when gross beta is greater than 10 times the yearly mean of control samples.

(c) Long-term composite samples are obtained from short-term composite samples at the specified locations.

(d) Composite samples are collected at Intervals not exceeding 2 hours2.314815e-5 days 5.555556e-4 hours 3.306878e-6 weeks 7.61e-7 months .

(e) Weekly milk sample from the Searight Dairy is analyzed for Iodine-131 only.

(f) Milk samples are collected bi-weekly when animals are grazing. The milk samples are collected monthly at other times.

(g) The fish samples contain whatever species are available.

IF adequate sample size Is available, THEN the sample Is separated according to species, and compositing will provide one sample of each species.

IF adequate sample size Is not available, THEN separation by species Is not practical. Therefore edible parts of all fish in the sample are mixed to provide one sample.

(h) Composite samples are obtained by collecting an aliquot at intervals not exceeding 2 hours2.314815e-5 days 5.555556e-4 hours 3.306878e-6 weeks 7.61e-7 months at location 2.1. The water treatment plant operator at location 5 obtains the weekly grab sample from the daily composite grab samples. For location 49, the weekly grab sample Is obtained by a field technician.

(i) Two (2) TLDs are collected quarterly from each monitoring location.

(k) Offsite Dose Calculation Manual procedure 1t2-ODC-3.03, Attachment Q, Table 3.12-1 requires three (3) dairies to be selected on basis of highest potential thyroid dose using milch census data. See Section 2-E of this report (Monitoring of Local Cows Milk) for specific locations sampled.

2-4

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report

2. Summary of Results All results of this monitoring program are summarized in Table 2-2. This table is prepared in the format specified by the NRC via the Branch Technical Position in NUREG-1301, and in accordance with Beaver Valley Power Station Offsite Dose Calculation Manual. Summaries of results of analysis of each media are discussed in Sections 2-B through 2-H and an assessment of radiation doses are given in Section 2-L Table 2-3 summarizes Beaver Valley Power Station preoprional ranges for the various sampling media during the years 1974 and 1975.

Comparisons of preoperational data with operational data indicate the ranges of values are generally in good agreement for both periods of time.

Activity detected was attributed to naturally occurring radionuclides, BVPS effluents, previous nuclear weapons tests or to the normal statistical fluctuation for activities near the Lower Limit of Detection (LU).

The conclusion from all program data is that the operation of the Beaver Valley Power Station has resulted in no significant changes to the environment.

3. Quality Control Program The Quality Control Program implemented by the Beaver Valley Power Station to assure reliable performance by the contractor and the supporting QC data are presented and discussed in Section 4 of this report

4. Program Changes The following changes were implemented in the 2005 sampling program.

During the period December 2004 through January 2005, the Global Positioning Satellite (GPS) system was used to obtain latitude, longitude, and elevation data at all sampling locations of the Beaver Valley Power Station Radiological Environmental Monitorng Prog . This information was also obtained for the locations identified in the 2005 Annual Land Use Census. Te GPS data was then transfed to a computerized topographic mapping pronam n order to obtain compass directions, sectors, and distances. This served as a erificaon of currently used data. No significant differences were found, however accuracy was improved. The referenee point for the sold" location data was the center of the Unit I Reactor Containment Building The reference point for the OPS data used the midpoint between the Unit I and Unit 2 Reactor Containment Buildings.

2-5

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Table 2-2 ENvWRONMENTAL RADIOLOGICAL MONITORING PROGRAM

SUMMARY

Name of Faclty: Beaver Vatby Power Station Untt I and UnIt 2 Docket No.: I0-3341/60413 Location Facilitry: BeaverCountv.epnsvanta Reporting Period: CalendarYear-2O5 Medium: Air Particulate and Radiolodine Unit of Measurement (piao Cweis /cubic mee T Number of Toal Number Untof etitdlarLocatons Locaions wM M~he Annual Mean Cont Location Nonroulne ofAnalysis teMcon empraction)" zz mean Pclors)" Name FlkaellonJ) Reped Peformd L D Wso Dtance and Orlon endDiRectio

__n __°tance ___em_

Graosssets 004 Q027 ( 4881488) No.30 8 ninport PA Q029 ( 6212 ) No. 48 MkbA WV 0.029 ( 162) NA 620 0.012 - 0.074 Cocs FenIy 0.012 - 0.074 Wter Tower 0.012 - 0.054 Sltation 'CofierWay QSD0ne ElNE 16.30 mfes SSW 1631 '40 LDW 0 148) LLD 0 1458) UD( 0 162) 0 20~

Gam 40 Be-7 NA 0.071( S61J6 ) No.l1A1uWpa, PA 0.074( 414 ) No.48 eton.WV 0.072( 414 ) NA 0047 - 0.09 8heffiskd 0.061 - 0.082 V1terrTawer 0.061 -0.08 Suacn CeWierr

.10mlss E 130 miles SSW Co400 0.003 LlD 018 ) LLD 0 136 LLD ( 0 14 ) NA Cs-134 0.004 LLD 0 136 ) UD( 0 136 ) LLD( 014 ) 0 Cs-137 O.C004 LLD 028 ) ULD( 01 ) LLD ( 0 14 ) 0 Ba-La-140 0.0005 LLD 0 136 ) LLD 01 36 LLD( 0 14 ) NA a Nomlnal Lower Limit of Detection b Mean and range based upon detectable measurements only.

Fraction of detectabel measurements atspeclfied locations is indicated In parentieses (fraction)

Nonmutine Reported Measurements (

Reference:

ODCM procedure tl2.ODC003, AttachmentQ, Control S.t2It)

NA a Not Appflcable (Naturally Occurring Radionuclides Not required by ODCU) 2-6

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Table 2-2 ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM SUIVIMAR Name of Facility: Beaver Valley Power Station unit I and Unit 2 Docket No.: pii-334a50413 Location of Facidiy: BeaverSounty. Pennsylvania Reporting Perlo CalendaiYear -2005 Medium: Duinldng Water UnLt*o Measurement pico Cures I Itet)

Too and Lwer Numlbrf TOtdAlNmber mtel Alldidkcr Locatons Leatons with HIlhest Annal Mean Controt Lcation Nonroullne

'fArdhyas Odecon Mean pmcton)SO Name Mean Iamctonrk Nan Mean ttMn)Q RRpftd Premwd LLae and 1iection Range D sta ceand Direction R e Me 0131 6 0643 ( 65 1104) No.4 MdUaPA 0547( 30D2 ) N. 49 b*y. PA OE5 ( 41 162 0 0.3 -12 VfterDepstmed .3 -12 Upablam of 0.3 - Z 156 1.2msNw MUontmeuyown

._ . 6.0 MIResNE

-4m 233( I/e No.49-Ea repcot OHl 2=f 1114 ) No.49tUstm lO9f 1 ) 0 12 20 223 - 233 - WikerDobner 233- 233 UormenyDam 199 - 199

4. nIesNWW .5._6_.0 ntis NE Gm J.

Mn-54 5 LLD ( 0 124 LLD( 0 24 ) LLD 0/12) 0 Fe-G9 10 LLD( 0 124 ) LD( 0 124 llD( 0 112) 0 Co-B LLD ( 0 124 ) LLD 0 124 ) LLD( 0 112) 0 Coa-o 6 LLD ( 0 124 ) LLD 0 124 ) LLD 0 l12) 0 Zn45 10 LLD ( 0 124 ) LLD( 0 124 ) LLD( 0 112) 0 20-NbO5 6 LLD ( 0 124 ) LD( 0 124 ) Ill( 0112) 0 Ce-134 5 LLD 0 124 ) LD( 0 124 ) LLD 0 112) 0 Ca-IS7 6 LLD 0 24 ) LLD 0 124 ) LLD( 0 112) 0 Ba4_R140 15 UD( 0 124 ) LLD 0 124 ) ID( 0 112) 0 a Nominal Lower LUmmit of Detection

'Mean and range based upon detectable measurements only.

Fraction of detectabel measurements at specilied locations Is Indicated In parentheses fraction)

'Nonroutlne Reported Meaurernents (

Reference:

ODCMI procedure 112-ODC-3.03, Aftachment Q.Control 12.1)

NA - NotApplicable (Naturally Occurring Radionuclides Not required by ODCMI) 2-7

Beaver Valley Power Station 2005 Annual Radiological EnvIronmental Operating Report Table 2-2 ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM

SUMMARY

Name of FacIdty Beaver Vallev Power Station UnK 1 nd Unit!

Docket No_ 600-334150-413 Location of Facility: Beaver County. Pennsybvanla Reportng Perlod: CalenidarYear-2005 Medium: Surface Water Unit of Measurement (pl Curwes I Eter)

Tvpemxl Lor Nunmeref Total Number of Atlldor Locatos Lcations a lgbestAnnual Hean Contl Locson Nonmud-ne ofIAyala A cion M. UnMean fain)" Name MGM praction)I Repeated hfaimed L R . Ot aDda eand gnctimn Raw Oisat8 and Direction RaMga" Meaurerf t U31 a5 0.885 ( 41 152 T No. 49 idustry, PA Oi5 ( 41 1 52 ) No.49 usby. PA 0.85 (41162) 0

.52 C.8-Sz - -2Upstresaat 0o-a3 upstraam of oa.za2. -

M.UomyDam DaM

_Motgmeay

_ __ __ _ _ _ _ _ _ m sN_

50 mases _ _ NE _ _ _8.0 ____moss_

H14 20 ULD 0 /t6 ) No.04 musNEy.PA 199 ( 1 14 ) Nix49 ktfiy PA 189 ( 1114 )

Upstream of 199 -109 Upstrewof 199 -199 12 M.. tgmeryDam Montoerey Dam 6.0 mIe NE _ 6.0 mkesE NE Gamm Ss.

Mn64 5 lD{ 0 124 ) UD ( 0 124 ) LLD( 0 112) NA Fe19 10 LLD 0 124 ) LlD ( 0 124 ) LLD( 0 112) NA Co-6 5 LLD ( 0124 ) .LD 0 124 ) LLD 0 112) NA Co60 5 LD( 0 124) LD( 0 124 ) U 0112) 0D( NA Zn45 10 LLD 0 124 ) LD( 0 124 LLD( 0 112) NA

&rNb45 6 UD( 0 124 ) UD( 0124 ) LLD 0112) NA Cs-134 6 LLD 0 124 ) UD( 0 /24 ) LLD 0 /12) MA C0-137 a LLD 0(o ) LlD( 0 124 ) UL( 0 It2) A Ba-14D 16 LD( 0 /24 llD ( 24 ) UD ( 0/12) NA

Nominal Lower Umit of Detection

' Mean and range based upon detectable measurements only.

Fraction of detectabel measurements at specified locations Is Indicated In parentheses (fraction)

' Nonroutlne Reported Measurements (

Reference:

ODCM procedure t2.0DC4.03, Attachment Q Control .12.1)

NA Not ApplIcable (Naturally Occurring Radlonuclides Not required by ODCM) 2-8

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Table 2-2 ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM

SUMMARY

Name of Facillty: BeaveryValev Power Station Unit I and Unit 2 Docket No.: 60-34 160I413 Location of Faciliyt BeaverCounty. Pennsytvanla Reporting Perlod: Calendar Ytear-2005 Medium: Grund Water Unit of Measurement (pico Curies I W e ad r. Numbef TWl Uumber nt A All bdictar Lctons Cons with ghest Annua Uin Conbol Locafon _Nonmlne eOAnalys Deacfdon Mean racima"l Nam ea frcaIon) Mean paction)" Reported Pufomrd N Ra ae and Chrecfon Range el and Iiecon Range Nase nts 8 D UJD { 0 14 ) UD ( 0 14 ) 68hVpkpow%PA IoI1 LDW( 0 12 ) 0

._ 0.5 nies NE Gamma NC11 ShWbiWt PA Q0 nizbs NE Mn-F4 5 LLD 0 14 ) UD( 0 14 ) LLD(O2)

FC489 10 LLD 0 4 ) UD (014 ) IJD(012) 0 Co604 5 LLD 0 14 ) UD( 014 ) llD( 0 12 ) 0 CZ-h 5 LLD 0/4) D( 0 14 ) D(0 12) 0 Zn-S 610 LLD 0U4 D 04 ) LD( 0 12 ) 0 Zr-N645 5 LLD( 014 ) LLD( 0i4 ) L ( 012) 0 Ce-134 5 UD( 014 ) L (0 14 ) LLD( 0 12) 0 Ca-137 5 LLD( 014 ) LLD( 014 ) UD( 012 ) 0 lA-La4I0 15 LLD 0/14 LLD 0(014 )LLD(012) 0 NNominal Lower Umit of Detection b Mean and range based upon detectable measurements only.

Fraction of detectabel measurements at specified locations Is Indicated In parentheses (fraction)

Nonroutine Reported Measurements (

Reference:

ODCM procedure 112-0DC-A03, Attachment Q.Control .12.1)

NA - Not Applicable (Naturally Occurring Radionuclides Not required by CDCM) 2-9

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Table 2-2 ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM SUMMARI Name of Factilly: BeaverYalley Power Station Unit I and Unit 2 Docket No.: i0-i6150413I Location of Faclty Beaver County, Pennsylvania Reporting Period: CalendarYear- 2005 Medlum: Precipitation Water Unit of Measurement ie Cures I ftor T nd Lower Number Total 1Nmber Uniftoat AldcatarLocutions 'Lcatlona IwNgh-t econtal Loc aion ContmlinNon o1Anabysis Detion eN qOW(t tonJ)Pi rean N= Mean (con)*i Re d M

Peronued UWM Rge 0 DErection Ditance end so O latance and Direction Rang

Ueaare_"

Ha 2W 411.25( 3/a ) Na.47East UpooI4OH 4siOD f 1 4 3 No.48akWn.LVW UDL 014 0 12 242 .490 WAer Depatnent 490 - 490 Wbbar Tower ColierW .ay

. 4.9 miles VM 16.30 mnils SSW Garnma 12 Un-44 6 UD( 01 ) UD( le ) LLD. 0 14 ) NA Co84 1 UD L ( 0 ) UO( O/le ) UD( 014 NA K

Co40 6 MD( 0/St UD( O/le ULD( 014 ) HA Co UO( O la 3

) 0 D( Ole LLD ( 0 /4 ) A Zn-I5 10 U.O 0/ o le ) LLD( 014 NA K

Zr4bW-O 6 LLD( O is LLD 0 tO ) UD( 0 14 ) NA Ce134 6 LLD 0(l ) LLD 0l 3

)D 0O4 ) NA Ce-IS7 5 LW( 0/is LLD 0/is LLD ( 0/14 KA Ba-140 15 LLD O0 lID( L a ) LLD( 014.) NA a Nominal Lmer Limit of Detection Mean M and lnge based upon detectable measurements only.

Fraction of datectabel aeasurements t Specified locations he hndicated In parentheses (fraction)

' Nonroutine Reported Measurements (

Reference:

ODCM procedure 1124ODC-L03. Attachment Q. Control 3.12.1)

NA - Not Applicable (Naturally Occurring Radionuclides Not required by ODCM 2-10

Beaver Valley Power Station 2005 Annual Radiological Environmental operating Report Table 2-2 ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM

SUMMARY

Name of Faclity: Beaver Valley Power Staton Unit I and Unit 2 Docket No.: 60-334/ 60413 Location of FacUty: Beaver County. Pennsulvanla Reporting Pedod. Calendar Year *2005 Medium: Milk Unit of Measuremeft (pica Curies I Ex)

Tpe alnd Lower untwmor Tota Nubmber t ef All hIdicator Locations Locstions wit, N gh W d Mean Contra] Laon Non__u_

Any Detection lemrction) 4 N Uenmmacton)m c rane e action)#4 Reported Peitrned Range PI Dstance and Dircton Rang _ ^ Distance and Direton Range easmerentstm e

1-131 0 O D 1)128) LLD( 01128) No.U6SSuWedswn PA Lim( 0 12D 0 148 WdsxheknerFerm 10.40 rIbes 8SW 6r49 20 llD( O 196 ) LLD ( 0 196 ) No.W 9OBu8rged PA LLD 0 120) NA 116 W rner Fam

__ __ _ _ _ _ _ _ _ _ _ 1 .40 m .eSSW _ _ _ _ _

8roS0 0.7 1J7( 91 196 ) No. 114 Hoiotwn, PA 2.30 ( 19I ) No. 06 8Qu9MdmmmiPA 1.09 (1120) NA 116 0.6 -6 MooreFenn 1.3

6 Whelr Fam 0.6 - Z1 2.12 mIbs SW 10.40 mWes 8SW Ga-116 K.40 NA 143 CS(9B IS ) No.114 Hoollown, PA 1486B9 19 119 ) No. 96 BWQettwn, PA 389 (20 120) NA 1147 - 1014 Moore Form 1258 - 1721 WndshelnerFwgm 1297 -1537 212 mWaesW 10.40 mba SSW Mn464 5 LLD 01 UL ( 019B ) LLD 0 120) NA Fe-W 10 LL( 0 19B ) LLD 019 ) UD( 0 120) NA Co48 6 U D( 019BSB .( .

0I ) LLD( 0 120) NA C060 6 ULLD 0 196 ) LLD 01 9 ) LD( 0 120) NA Zn-65 10 LD ( 019 ) LlD( 0 196 ) LD ( 0120) NA Z4Jb45 5 LD ( 06 ) LD ( 0 196 )

L LLD 0 120) NA Cs134 6 LLD 019 ) LD ( 0 196 ) LlD( 0 120)

Cs-137 5 LD( 0196 ) LLD 0 19 ) LD( 0 120) 0 8a4A-140 15 LDW 019 ) ULLD 0196 ) . LD( 0120) 0

- aominal Lewer Umn or uevecuun b Mean and angbased upon detectable measurements only.

Fraction of detectabol measurements at specified locations bs Indicated In parentheses (fracton)

' Nonroutine Reported Measurements (

Reference:

ODCM procedure 112-0DC4.03, Attachment Q. Control &2ILI)

NA - Not Applicable (Naturally Occuring Radionuclides Not required by 00CM) 2-11

A

-Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Table 2-2 ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM

SUMMARY

Name of Facility: Bemver Valley Power Station Unit and Unit 2 Docket No.: 50334f 600413 Locaiton of Facilty: Beaver County. Pennsylvanla Reporting Period: CalendarYear -2005 Medium: Fish Unit of Measurement: (po Curies Igram) Wet Typ and NuMberef Totl nmber nat d All hdcatorLocatlon Locaions with Hihest Annual Mean Contol Location Nonraffne df Analysl t on eanpfaclon)i Name mean (WoO)P Name Meanactionl)W R d erfomead LWUN RauN Distance landOfnlcain RanP N an"m hrection Raw murenanents W.4 0.05 LLD 0i14 ) .'UD( 014 ) .LD(0I4) 0 Fe4o6 0.10 UD( 014 ) LLD 014) LLD 014) 0 Corl 0.05 LD( o04 ) LLD( 014 ) ULD 014 ) 0 C4-0 0.05 LLD( 014 ) LLD( 014 .LD( U oj4 ) 0 Z"S4 0.o LLD 0 14 LLD ( 0 14 ) UD( 014 ) 0 Zr-Nb-OS 0.03 LLD 0 14 )LD( 0 14 )LLD(014) 0 Ce134 0.0 LL( 014 ) LLD 014 ) LLD 014 ) 0 Cs-137 06 LLD( 014 ) LLD( 014 ) LLD( 014) 0 3e-La-140 0.07 LLD( 0 14 3LLD( 0 14 3LLD( 0 14 )0

Nominal Lower Umit of Detection

'Mean and range based upon detectable measurements only.

Fraction of detectabel measurements at specified locations Is Indicated In parentheses (fraction)

' Nonroutine Reported Measurements

Reference:

ODCM procedure 11200C4.1031 Attachment Q. Control &LI)

NA a Not Applicable (Naturally Occurdng Radionuclides Not required by ODCM) 2-12

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Table 2-2 ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM

SUMMARY

Name of Facility: Beaver Valley Power Station Unit 1 and Unit 2 Docket No.: W0M 160-413 Location of Facflit: Beaver County. Pennsylvania Reporting Period: Calendar Year -2005 Medium: Foodcrops Unit of Measurement (pc Curies I granm) t Typed ' ioiunier Total Uaner Umit of AU bdlcator Locaions Locatlons with Hgbest Annual Mean Control Loaton Nonrautine elAnalpla Deecln oan pacdonN Nean (fract-on)" mMu racn on)" Reported d LID Range DOtance and ODrection RangaDament aitio and Range Meas 1-131 0.06 LLD 03 ) UD( 013 ) UD ( Oi/ ) 0 4

Gamma 4

K40 NA l09 a /a ) No.46 hkinly.PA15D52 L809( It/ ) No. 48a Whbtn,WV 229( 11 ) NA 1.9-Z.99 Z5mbil6sNE Z99-ZES9 WahonArea 229-229 16.30 mba SSW M64 0.05 LLD( 0I ) LLD 013 ) UD( 011 ) NA Fe-W 0.10 LLD( 0I ) LLD 0/J ) UD( 0/1 ) NA Co-48 0.05 LLD 0/3 ) LLD 0/1 ) LLD( 011 ) NA Co-s 0.05 LLD( 013 ) LLD 013 ) LLD( 01 ) NA Znh85 0.10 03 ) LLD 0/J ) LLD( 0/1 ) NA Zr-Nb95 0.03 LLD OJ ) LLD( 0IJ ) LUD( 01 ) NA Ce-134 0.0Q UD( 013 ) LUD( 0IJ ) LLD( 01 ) 0 Cr-137 0.05 UD( 013 ) LLD( 0I ) LLD( 01 ) 0 Ba4o-140 0.07 LLD( 013 ) UD( 0I3 ) UD( 0/1 ) NA a Nominal Lower Uimit of Detection b Mean and range based upon detectable measurements enly.

Fraction of detectabel measurements at specified locations Is Indicated bI parentheses (fraction)

Nonroutine Reported Measurements

Reference:

00CM procedure V20DC0C.03, Attachment Q. Control 3.1Z1)

NA mNot Applicable (Naturally Occurring Radionuclldes Not required by ODCb) 2-13

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Table 2-2 ENVIRONMENTAL RADlOLOGICAL MONITORING PROGRAM

SUMMARY

Name of Facility: BeaverValley Power Station Unit I and Unit 2 Docket No.: 50W334/60413 Lcation of Faclty: BeaverCounty. Pennsylvania Reporting PerbodI: Cafendar Year -2005 Medium: Feedstuff it of Measurement (pico Cures I gram) We Type am Lwe Totl Nimiber 1 ? AN d/or Locations Loc OM Ngtee Annu ean Cot Lond ___ Nnioune eofnAyuls D n Mea fracton)O N Mean ffracuon)N Man MUMl-)" d Pefonend 1LW Ran Distance and rtion R t _______ dance and ODto Rae easenentsr 12

- e-7 NA 1.17( 6 112 ) N1 25 SeeWt Fann 1.17 ( 8 112 ) No. 25 Searst Farm 1.17 ( 6 112) NA

0. - 175 Hooitn, PA 0.3-Z7S H Q3- 175

.3PA 948 McCley Road 948 MUdeary Road 2.1 mies 8SW 21 maniSSW K40 NA 923 ( 12 1 12 ) No 25 earhtFwm 9.23 ( 12112 ) No. 25 SerhFm n23 ( 121 12) NA 0or2- 1.93 HoownPA 0.2- 13.93 Hookftwx PA 0.92-1293 948 McCey Road a948cCsay Road Z lnbs&SW 21 mD" SSW Mn44 0.06 LLD 0 112 ) UD ( 0112 ) LLD( 0 112) NA Fe-9 .10 UD( 0112 ) UD ( 0112 ) LLD 0112) NA Co45 0.06 UD( 0112 ) UD ( 0112 ) LLD 0112) NA Co4 0.05 110 ( 112 ) LLD 0 112 ) LID( 0112) NA ZAn5 0.10 lD( 0 112 ) LLD 0 112 ) LLD 0 112) NA Zr-Nb45 0.03 ID( 0 112 ) UD( 0112 ) UD 0 112) NA C-134 0.06 UD ( 0 12 ) LLD 0 112 ) LLD 0 112) NA CB-137 0.06 LLD( 0112 )D 0)12 )UL 0112 NA Ba4.L-140 0.07 LlD( 0 12 ) LLD 0 112 ) LL( 0112) NA Nominal Lower UmlN of Detection b Mean and range based upon detectable measurements only.

Fraction of detectabel measurements at specified locations Is Indicated In parentheses (fraction)

' Nonroutine Reported Measurements (

Reference:

ODCM procedure 1/2ODC-A03, Attachment 4 Control 312.1)

NA - Not Applicable (Naturally Occurring Radionuclides Not required by 00CM) 2-14

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Table 2-2 ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM

SUMMARY

IUame af

.Sw _ FaPcltv:-

,,. RBavrv Vaidlo w", _, Poemir

. _,._.Stftnn Unit

_ _ 1 amnd

_ _inHt. 2 Dpocket No.: 60S4i /60l413 Location of Facliy: Beaver County. Pennsytvanla Reporting Period: Calendar Year - 2005 Medium: Sediment (page 1 of 2)

Unit of Ueasurement (piCO Curies Igram) Dry Total nber Jit A3 hdarLocatior a withist 0AnulMe rIEcatimon _lonronu fAnalyls DeteconM ona -ean onr)X mu (rcalon3 d W

a DireOcon Rnd e toaan .

nd DIrecon Range " M eastaumeic 6

K4O NA 11.7( 4 14 NoW 50 Nea Cumbearn WV 1Z48 ( 2 1 2 ) Na.49a h1dfty, PA 12( 2 12 NA 10.16 - 12.89 Updtrea o 12.06 - 12.s Upsem at 5.76 - 1521

,Oam monigomy Dam 11.6 mIlesWSW 6 mIba NE 0.05 LLD( 014 llD( 014 ) LLD( 0 12 NA

.10 LLD 014 LLD 014 LLD ( 012 NA Co4B 005 QS2 2 1 4 No. 2A BVPS Q32 C 2 1 2 No. 49a hidusy, PA LLD ( 012 NA 0,11 - 0.3 OutFat .11 - 0.53 Uprem of Vk* UMrgmazy Dam 02 mbs W 5 mles3 NE Co4O 0.05 0.235( 2 1 4 No.2A 6VPS 0.235 ( 2 1 2 No. 49a IPdutry.PA UD ( 0 12 ) NA 011 -0QS6 OutFall 0.11 -0.25 Uptem o M-m D 0.2 mWes W 6 mies NE Zn65 .10 LILD( 0 14 LLD( 014 LLD ( 012 ) NA Zi5 0.03 ULD 014 LLD 014 LLD ( 0 12 ) NA Nb-65 0.03 LLD 014 LLD 0 14 LD ( 0 12 ) NA Ca-134 0.5 ULD( 014 ULD( 0 14 LLD ( 012 ) NA CrA37 0.05 Q101 ( 3 1 4 No. 60 NewM Cnbwnk WV 0.13 ( I 1 2 ) No. 49a bdustry,PA Q0754 ( 2 1 2 ) NA 0.063 - 0.13 Upstaam of 0.13 - 0.13 Upstrem O D06- Q091 Dam Momtmery Dam 11.6 milesWSW 6 mibs NE sA-140 0.07 UD( 014 llD( 014 LLD( 0 12 ) NA NA 0.36( 4 1 4 No 60 Now Csnbeen4 WVt Q.365 2 1 2 I No. 49a hkiuy PA 0.325 ( 2 1 2 )

0.34 - 0.39 Upteab of 0.34- QOg UpS"= of 026 - 0.39

) Dam Uabftwgwy Dam 11 mAles WSW 6 mfles NE

-14 NA Q83 ( 4 1 4 No. 60 New COmawebe VW MOSS ( 2 1 2 ) No. 49a xdshtry, PA 0745 ( 2 1 2 ) NA 0.61 - 0.2 Upstbem 081 - 0.2 Upeam at 67 - 0.o2 Dam Motgomery Dam 11.6 mes WSW 5 mbes NE Pb-212 NA 1.253( 4 1 4 No S0 NowCWnbdenta WV 129 ( 2 1 2 II No. 49a ifdstr, PA MOS5 ( 2 1 2 ) NA 1.0 - 1.43 Upstrem of 1.15- 1.43 Upseam of 0.92- 1.01 Dam U e Dam 116 me WSW 6 mfbs NE

& I I 2-15

Beaver Valley Power Station 2005 Annual Radolofgical Environmental Operating Report Table 2-2 EN RONMENTAL RADIOLOGICAL MONITORING PROGRAM

SUMMARY

Name of Facdty: eaverVaiiev Poweritation Unit I and Unit 2 Docket No.: 60W34 t 6043 Location of FacilIt. BeaverCounty. Pennsyhmnla Repoding PerSod: QAendarYear-2005 Medium: Sediment (ae 2 of 2)

Uit of Measurement fpco Curios Igra) Mty Type and .lwr umkTf Totl Niumber ltdef lnicacatons c fib wM NOW umean Camfrl Locaffon _Conoun dOnalns Detc Man hPcMnt -W mean mmmucn)4i WMS mean cuoniW R d ponned L Rang_

J1° 0 Dla d d0redlon Distanceand Okion Ran eas Pb-214 MA 0.987( 4 1 4 1 No. 60 NMCwbl _ WV 1.Q2 ( 2 1 2 ) No. 49a kARy. PA 0Q61 (2 1 2) NA 0.93 - 1.09 Upsheam f G- 109 0.0 Upswea of 0A8 - (04 Dam Hmnsy Dam t1.t mlWesYW . WaisNE Ra-2= NA W( 4 1 4) No.M60NeMCmberdVN( 2.39(2 1 2 ) No49a khtsy,PA 1.A( 12) NA 1.96-169 Ut1amof Z09 - 269 Upatmdnof 1.6 - 1.6 DMn- UWQMoIyDan 11 mD"es WMW - 5esNE

>-228 NA 1.2( 4 1 4 ) No.60NewbmrnmbetnWV 125( 2 1 2 ) No.49ahkamy, PA 1.11 ( 1 1 2) NA RS78 - t.ST UpWream 1.22-1.23 Upshond of 0.095- 1.27 Darn MtmeryDam .

. _11A mlesWSW _ _mg" NE

Nominal Lower Lhmit of Detection b Me and lange based upon detectable measurements only.

Fraction of detectabel measurements at specified locations Is Indicated In parentheses (fraction)

Nonroufne Reported Measurements (

Reference:

ODCMA procedure 112U00DC4A3, Attachment 04 Control 312.1)

MA - NotApplicable (Naturally Occurring Radlonuclides Not required by ODCM) 2-16

Beaver Valley Power Staon 2005 Annual Radiological Environmental Operating Report Table 2-2 15WRONMENTAL RADIOLOGICAL MONITORING PROGRAM

SUMMARY

Name of Facilliy: Beaver Vallev Power Station Unit I and Unit 2 Docket No.: 60340160A413 Location of Facility: Beaver Countv. Pennsylvania Reporting Period: Calendar Year - 2n06 Medlum: Soil Unit of Measaurement (co Cubies I am) Dry Type and .Lower Totl Number Uihof AllAD I . J IIINun__of IndtcrIoanns ' 0t5 HlWhat Annual Mean Conbtl Location Nonwuftne 0

ofAnalyalh Meanpaction)II dDetection NAMe I-UeMam an n Pwned UDW RW Distnce andoon RDisance end Direction Meau rements G amm a I __ _ _ _ _ _ _ _ __ _ _ __ _ _ __ _ _ _ _ _

Note: Soil Sampling performed every Ihree (3) years. Sampl ng was performed In 2003, and Is next due In 2006.

K40 Un44 Fe_

0048 Co4O zr-95 Nb-05 Ca-134 Ce-I37 fla-Le-140 TI-M0 Pb-212 Pb-2114 fte-22

' Nominal Lower Umit of Detection b Mean and mange based upon detectable measurements only.

Fraction of detectabel measurements at specified locations ks Indicated In parentheses (faction)

' Nonroutlne Reported Measurements (

Reference:

ODCM procedure 1l2.0DC403. Atachment Q0Control 3.121)

NA a Not Applicable fNaturally Occurring Radionuclides Not required by 0DCM) 2-17

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Table 2-2 ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM

SUMMARY

Name of Faclily. BeaverVaT1ev Power Station UnIt I and Unit 2 Docket No.: IQ34 1S(13 Location of Faceility Beaver County. Pennsvtvanla Reporting Period: Calendar Year -2006 Medium: External Radlailon Unit of Measurement: (MRIQuarleij TMO and Lower Nbrof Toeal N11rbr UInitef tAdlcoaar to catlons am Hi t Annudl mean Conal lcation __ nmutina ef Anairdu tection r Meanputhionift HNae men ractionJV ama Mean iaction)k R t Perfoied LLD Row _ _ _ __ _ dan__and Drection R__ Distance and Dntion Ranges n Nmen GaIMM 46 1-4 ( 492 - 492) N 112 BVPSSie 22A ai a 8 No.48 brton, WV 19.4 ( 811 ) NA 60 11.7 - 24.7 Paretr 2.1- 24.7 VkwTow 19.0 - 20.

Location CooriYby a Nominal Lower Limit of Detection Mean M and range based upon detectable measurements only.

Fraction of detectabel mreasurements at specified locations Is Indicated In parentheses (fraction)

' Nonroutine Reported Measurements (

Reference:

ODCM procedure 112-ODC4D03, Attachment Q.Control 12.I*)

NA - Not Applicable (Naturally Occurring Radionuclides Not required by OCM) 2-18

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Table 2-3 Pre-Operational Environmental Radiological Monitoring Program Summary Name of Facility: Beaver Valley Power Station Docket No.: 50-334 Location of Facility: Beaver County. Pennsylvania Reporting Period: Calendar years 1974 - 1975 Medium or Pathway Analysis and Total Lower Limt All Indicator Locations Sampled Number of Analysis of Detection Mean, (f) Range (Unit of Measurement) Performed (LLD)

Sediments Gross Alpha (0) -

(pico Curie /gram) dry Gross Beta (33) 1 18 (33/33) 5-30 Sr-90 (0) -

U-234, 235,238 (0) _ _

Gamma (33) - 13 (33/33) 2 -30 K-40 1.5 13 (33/33) 2 -30 Cs-137 0.1 OA (21/33) 0.1 -0.6 Zr/Nb-95 0.05 0.8 (12/33) 0.2 - 3.2 Ce-144 0.3 0.5 (3/33) OA - 0.7 Ru-106(a) 0.3 1.5 (3/33) 1.3- 1.8 Others - <LLD Foodstuff Gamma (8) -

(pico Curie /gram) dy K-40 1 33 (8/8) 10 - 53 Cs-137 0.1 0.2 (1/8) -

Zr/Nb-95 0.05 0.2 (1/8) -

Ru-106(a) 0.3 0.8 (1/8) -

Others - < LLD Feedstuff Gross Beta (80) 0.05 19 (80/80) 8 -50 (pico Curie /gram) dry Sr-89 (81) 0.025 0.2 (33/81) 0.04 - 0.93 Sr-90 (81) 0.005 OA (78/81) 0.02 - 0.81 Gamma (81) -

K-40 1 19 (75/81) 5-46 Cs-137 0.1 0.5 (6/81) 0.2- 1.6 Ce-144 0.3 1.5 (5/81) 0.9 -2.6 Zr/Nb-95 0.05 0.8 (13/81) 0.2- 1.8 Ru-106(a) 0.3 1.A (12/81) 0.6 - 2.3 Others < LLD Soil Gross Alpha (0) -

- Template Samples - Gross Beta (64) 1 022 (64/64) 14-32 TepieSmls Sr-89 (64) 0.25 0.4 (1/64) -

(pico Curie/gram) dry Sr-90 (64) 0.05 0.3 (48/64) 0.1 - 1.3 U-234, 235, 238 (0) - _

Gamma (64) -

K-40 1.5 13 (63/64) 5 -24 Cs-137 0.1 1.5 (56/64) 0.1 - 6.8 Ce-144 0.3 1.1 (7/64) 0.2 -3 Zr/Nb-95 0.05 0.3 (13/64) 0.1 -2 Ru-106(a) 0.3 1.1 (3/64) 0.5 -2 Others _- <LLD d(f) Fraction of detectable measurements at specified location.

2-19

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Table 2-3 (Continued)

Pre-Operational Environmental Radiological Monitoring Program Summary Name of Facility: Beaver Valley Power Station Docket No.: 50-334 Location of Facility: Beaver County. Pennsylvania Reporting Period: Calendar years 1974 - 1975 Medium or Pathway Analysis and Total Lower Limit All Indicator Locations Sampled - Number of Analysis of Detection Mean, (f) Range (Unit of Measurement) Performed (II D)

Son Gross Alpha' (0) -

- Core Samples - Gross Beta (8) I 21 (818) 16 -28 Q~c xi ga)dy Sr-89 (8) 0.25 <* LL.n (Pico Curie / ) d90 (8) 0.05 0.2 (518) 0.08-0.5 Gamma (8) -

K-40 1.5 13 (8L8) 7-20 Cs-137 0.1 1.2 (7/8) 0.2 -2.4 Co-60 0.1 0.2 (1/8) -

Others _ <LLD SurficeWater GrossAlpha (40) 0.3 0.75 (5/40) 0.6-1.1 (Pico Curie / liter) Gross Beta (120) 0.6 4.4 (120/120) 2.5 - 11.4 Gamma (1) 10-60 < LLD Tritium (121) 100 300 (120/121) 180 - 800 Sr-89 (0) -

Sr-90 (0) -

C-14 (0) - _

Drinking Water I-131 (0) - _

(Pico Curie / liter) Gross Alpha (50) 0.3 0.6 (4/50) OA - 0.8 Gross Beta (208) 0.6 3.8 (;208208) 2.3 - 6A Gamma (0) -

Tritium (211) 100 310 (211/2ll) 130-1000 C-14 (0) -

Sr-89 (0) _

Sr-90 (0) -

Ground Water Gross Alpha (19) 0.3 <LLD (pico Curie / liter) Gross Beta (76) 0.6 2.9 (7375X)b) 1.3 - 8.0 Tritium (81) 100 440 (77/81) 80 - 800 Gamma I (1) 10-60 <LLD Air Particulates Gross Alpha (188) 0.001 0.003 (35/188) 0.002- 0.004 and Gaseous Gross Beta (927) 0.006 0.07 (927/927) 0.02 -0.32 (pico Cnie /cubic meter) Sr-89 (0) -

Sr-90 (D) -

1-131 (816) 0.04 0.08 (2J816) 0.07 -0.08 Gamma (197) -

ZrfNb-95 0.005 0.04 (122/197) 0.01 -0.16 Ru-106 0.010 0.04 (50/197) 0.02-0.09 Ce-141 0.010 0.02 (3/197) 0.01-0.04 Ce-144 0.010 0.02 (44/197) 0.01 - 0.04 others <LIlD (f) Fraction of detectable measurements at specified location.

2-20

- Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Table 2-3 (Continued)

Pre-Operational Environmental Radiological Monitoring Program Summary Name of Facility: Beaver Vlley Power Station Docket No.: 50-334 Location of Facility: Beaver County. Pennsylvania Reporting Period: Calendar years 1974 - 1975 Medium or Pathway Analysis and Total Lower Limit Al Indicator Locations Sampled Number of Analysis of Detection Mean, (f) Range (Unit of Measurement) Performed Milk 1-131 (91) 0.25 0.6 (4/91) 03 -0.8 (pico Curie 1liter) Sr-89 (134) 5 7 (4/134) 6- 11 Sr-90 (134) 1 5.3 (132/134 1.5- 12.8 Gamma (134) - )

Cs137 10 13 - 11-16 Others (19/134)

<LLD External Radiation y - Monthly (599) 0.5 mR* 0.20 (599/599 0.08 - 0.51 (milli Roentgen /day) y - Quarterly (195) 0.5 mR*. 0.20 ) 0.11 - 0.38 Annual (48) 0.5 mR* 0.19 (195/195 0.11 -0.30

- -(48148)

Fish Gross Beta (17) 0.01 1.9 (15/17) 1.0-3.2 (pico Curie gram) wet Sr-90 (17) 0.005 0.14 (17/17) 0.02 - 0.50 Gamma (17) 0.5 K-40 - 2.4 (17/17) 1.0-3.7 Others <LLD

LLD in units of mR - Lower end of useful integrated exposure detectability range for a passive radiation detector (TLD).

(a) May include Ru-106, Ru-103, Be-7.

(b) One outlier not included in mean. (Water taken from dried-up spring with high sediment and potassium content. Not considered typical groundwater sample).

(I) Fraction of detectable measurements at specified location.

2-21

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report B. Air Monitoring

1. Characterization of Air and Meteorology The air m thevicinity ofhe site contains pollutants typical for an industrial area. Air flow is generally from the southwest in summer and from the northwest in the winter.

2. Air Sampling Program and Analytical Techniques

a. Program The air is sampled for gaseous radioiodine and radioactive particulates at each often (10) offsite air sampling stations. The locations of these stations are listed in Table 2-1 and shown on amap in Figure 2-1.

Samples are collected at each of these stations by continuously drawing two cubic feet per minute of atmosphere air through a glass fiber filter paper and a charcoal cartridge. The glass fiber filter paper is used for collection of airborne particulates, while the charcoal cartridge is used for collection of radioiodine. Samples are collected for analysis on a weekly basis.

The charcoal cartridge is used in the weekly analysis of airborne Iodine-131. The glass fiber filter papers are analyzed each week for gross beta, then composited by station each quarter for gamma spectrometry analysis. In order to reduce interference from short-lived naturally occurring radioactivity (e.g.; radon and thoron), the glass fiber filter papers are decayed prior to performing beta analysis in a low background counting system.

b. Procedures Gross Beta Analysis of Filter Paper: Analysis is performed by placing the glass fiber filter paper from the weekly air sample in a 2 inch planchet and analyzing it in a low background, gas flow proportional counter.

Gamma Emitter Analysis of Filter Paper Analysis is performed by stacking all of the glass fiber filter papers collected from each monitoring station during the quarter and scanning this composite on a high resolution germanium gamma spectrometer.

Iodine-131 Analysis of Charcoal Cartridge: Analysis is performed by a gamma scan of each charcoal cartridge.

2-22

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report

3. Results and Conclusions A summary of data is presented in Table 2-2.

a. Airborne Radioactive Particulates A total of five-hundred4wenty (520) weekly samples from ten (10) locations were analyzed for gross beta. Results were comparable to previous years. Figure 2-2 indicates the weekly average concentration of gross beta in air particulates.

The weekly air particulate samples were composited into forty (40) quarterly samples which were analyzed by gamma spectrometry. Naturally occurring Beryllium*7 was identified in forty of forty (40 of 40) samples. No other radionuclides were detected. A summary of the analysis results during the report period are listed in Table 2-2. A trend graph of analyses (including the pro-operational period through the report period) is shown on Figure 2-2.

The ten air particulate filters for the week of 10/03/05 through 10/10/05 were misplaced by the contractor laboratory prior to analysis for gross beta. The gross beta data results for this week were determined by assuming an average from the previous and the following weeks. This condition and associated Corrective Actions are documented in Condition Report No. CRO5-00050-01.

Based on the analytical results, the operation of Beaver Valley Power Station did not contribute any measurable increase in air particulate radioactivity during the report period.

b. Airborne Radioiodine A total of five-hundred-twenty (520) weekly charcoal filter samples were anablyed for Iodine-13 1. No detectable concentrations were present at any locations.

Based on analytical results, the operation of Beaver Valley Power Station did not contribute any measurable increase in airborne radioiodine durng the report period.

c. -Upgrade of Trip Circuits on Sample Stations During the report period, the ten air particulate and radioiodine sample stations were upgraded from 8 ampere trip circuits to 15 ampere trip circuits. This condition and associated Corrective Actions are documented in Condition Report No. CR05-05888-01.

2-23

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Figure 2-1 Environmental Monitoring Locations - Air Sampling Stations Site Distance Sanple Type No. Sector (mites) Sample Point Descrption 13 11 1.4 Hookstown, PA (Old Meyer Farm) 27 7 6.1 Aqulppa. Pa (Brunton Farm) 28 1 8.6 Sherman Farm 29B 3 8.0 Beaver. PA Friendship Ridge)

AMrPartlculate 30 4 0.5 Shlppingport, PA (Cook's Ferry Substation)

& Radiolodine 32 1S 0.8 Midland, PA (North Substation - Rt 68) 46.1 3 2.3 Industry, PA (MdKeels Service - RL 68) 47 14 4.9 East Liverpool, OH (Water Department) 48 10 16.3 WeVton, WV( Water Tower, Collier Way) 51 5 8.0 Aliquippa, PA (Sheffield Substation) 2-24

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Figure 2-2 Graph of Annual Average Concentration: Gross Beta in Air Particulates Beaver Valley Power Station REM P Environmental Air Particulate Samples - Gross Beta 0.20 0.18 -

A Average of 9 hIdicator Locations U 0.16 -

- -A--- Control Location 0 0.14 - Pre-Operational value (0.07 pa I cubic rreter)

-a 0.12 - -eRequired LLD (0.01 pCi / Iter)

E 0.10 -

NNo Reporting Level for Gross Beta

.U 0.08 -

.0 0.06 - -_ ____ __ _A_ _ ___ _

0 0.04 - -- - - - - - - - - - - - - - - - - - - - - - _ _ -_ -_ -_ -_--

a.

0.02 -

0.00 -

kAb N91 15 I I I I 0 I I I I I 2-25

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report C. Monitoring of Sediments and Soils I Characterization of Stream Sediments and Soils The stream sediments consist largely of sand and silt. Soil samples may vary from sand and silt to a heavy clay with variable amounts of organic material.

2. Sampling Program and Analytical Techniques

a. Program River bottom sediments were collected semi-annually above the Montgomery Dam, in the vicinities of the Beaver Valley discharge and above the New Cumberland Dam. A Ponar or Eckman dredge is used to collect the sample. The sampling locations are also listed in Table 2-1 and are shown in Figure 2-3.

Soil samples are collected every three years. They were collected at each often (10) locations during 2003 and are not due to be collected until 2006. At each location, 12 core samples (3" diameter by 2" deep) are gathered at prescribed points on a 10 foot radius circle. Each location is permanently marked with reference pins. Each set of samples is systematically selected by moving along the radius in such a manner as to assure representative undisturbed samples. Sampling locations are listed in Table 2-1 and are shown in Figure 2-3.

Bottom sediments and soils are analyzed for gamma-emitting radionuclides.

b. Analytical Procedures Gamma Emitter Analysis of Sediment or Soil: Analysis is performed in a 300 ml plastic bottle, which is analyzed by gamma spectrometry.

2-26

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report

3. Results and Conclusions A summary of the analysis results during the report period are listed in Table 2-2. A trend graph of analyses (including the pre-operational period through the report period) is shown on Figure 24 and Figure 2-5.

a. Sediment A total of six (6) samples were analyzed by gamma spectrometry. Naturally occurring Potassium40 was detected in six of six (6 of 6) samples. Naturally occurring Radium-226 was detected in five of six (5 of 6) samples. Other naturally occurring radionuclides were also identified in most of the samples.

Cesium-137 was identified in five of six (5 of 6) river sediment samples. SINCE Cesium-137 was identified in both upstream and downstream samples, THEN it was not due to plant effluent releases (i.e.; from previous nuclear weapons tests).

Cobalt-58 was identified in two of six (2 of 6) river sediment samples. Cobalt-60 was also identified in two of six (2 of 6) river sediment samples. The samples that indicated Cobalt-58 and Cobalt-60 were obtained at the shore line of the main outfall facility. Identification of Cobalt-58 and Cobalt-60 at this location is not unusual, because the plant discharges Cobalt-58 and Cobalt-60 in liquid waste effluents. Specifically, the activity detected at this sample location is consistent with discharge data of authorized liquid effluent releases. All liquid effluent releases during the report period did not exceed the release concentration limits set forth in the Offsite Dose Calculation Manual.

b. Soil Soil is sampled every three years and was sampled in 2003. Soil sampling will be performed during calendar year 2006.

2-27

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Figure 2-3 Environmental Monitoring Locations - Shoreline Sediments and Soil byr : - /--- i --

Sample Site Distance Type No. Sector (miles) Sample Point Description 13 11 1.4 Hookstown, PA (Old Meyer Farm) 22 8 0.3 South of BVPS, Transmission Lines 27 7 6.1 Aliquippa, PA (Brunton Farm) 29A 3 8.3 Beaver, PA (Nicol Farm)

Soil 30a 4 0.5 Shippingport, PA (Cook's Ferry Substation) 32a 15 0.8 Midland, PA (North Substation) 46b 3 2.5 Industry, PA (Willows Inn - Rt. 68) 47a 14 4.9 East Liverpool, OH (Water Department) 48A 10 16.3 Weirton Water, WV (Tower, Collier Way) 51a 5 8.0 Aliquippa, PA (Sheffield Substation) 2A 13 0.2 BVPS Outfall Vicinity Sediment 49a 3 5.0 Industry, PA (Upstream Montgomery Dam) 50 12 11.8 New Cumberland, WV (Upstream of Dam 2-28

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Figure 2-4 Graph of Annual Average Concentration: Cesium-137, Cobalt-58 & Cobalt-60 in Sediment Beaver Valley Power Station REMP Cs-137 Sediment Trends - Outfall Vicinity 1000.00 100.00I- - --. --- Cs-137 _____________________

A Control Location Cs-137 Pre-Operational Cs-137 (0.4 pCi I gram)

E - Cs-137 Required LLD (180 pCi/gm) 10.00 - - - - - - - - - - - - - - _No

- - Reporting Level for Sediment - -- - - - -- - - - -- - - - - - -- - -

CD) 0.01 Beaver Valley Power Station REMP Co-68 & Co-60 Sediment Trends - Ouffall Vicinity 100.00_ _ _ _ _ _ _ _ _ _ _ _ _ _

Co-58 1U nl 2 Pre-Operational Mean: Co-58 (0.098 pcVgm)

A 00-60 LUnnt2 Pre-Operalonal Mean: Co-60 (0.40 pCilgram)

-No Raqukred LLD for Co-58 or 0o-60

-No Reproting Limntfor Co-58 or Co-60 a / X A 1.00 ---------------- ---------- -- - \ tN -------

A&I \i /s AU A// v/^ *

.10 !\ A 0.o1 -

0.01 11, "

2-29

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Figure 2-5 Graph of Annual Average Concentration: Cesium-137 in Soil Beaver Valley Power Station REMP Cs-137 Soil Trends (Tri-Ennial) 1.2

1.0-- Control Location

\e-operational P Cs-1 37 (1.2 pa / gram) 0 0.4 - - - - - - - - -- - - - - - _______

0.0 01ib, 2-30

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report D. Monitoring of Feed Crops and Food Products

1. Characterization of Farm Products According to the 2002 Census of Agriculture (1), there were 645 farms in Beaver County. Total market value of production (Crops and Livestock) was $10,828,000.00. Some of the principal sources of revenue (>$100,000.00) are as follows:

Milk and Other Dairy Products from Cows $4,719,000.00 Cattle and Calves $1,387,000.00 Nursery, Greenhouse, Floriculture and Sod $1,129,000.00 Other Crops and Hay $893,000.00 Vegetables, Melons, Potatoes and Sweet Potatoes $843,000.00 Grains, Oil Seeds, Dry Beans and Dry Peas $567,000.00 Poultry and Eggs $523,000.00 Cut Christmas Trees, and Short Rotation Woody Crops $285,000.00 Fruits, Tree Nuts and Berries $198,000.00 Other Animals and Other Animal Products $85,000.00 Horses, Ponies, Mules, Burros, and Donkeys $81,000.00 Sheep, Goats and their Products $60,000.00 Hogs & Pigs Undisclosed Amount Aquaculture Undisclosed Amount

2. Sampling Program and Analytical Techniques

a. Program Representative samples of Feed Crops (cattle feed) are collected monthly from the nearest dairy farm (Searight Dairy). See Figure 2-6. Each sample is analyzed by gamma spectrometry.

Food products (vegetables) are collected at garden locations during the growing season.

Leafy vegetables, (e.g.; cabbage) are obtained from Shippingport, Georgetown, and Industry, Pennsylvania. Samples are also obtained from the control location in Weirton, West Virginia. All samples are analyzed for gamma emitters by gamma spectrxmetry.

Samples are also analyzed by radiochemical analysis for Iodine-131.

http://www.nass.nsdagov/census/censusO2/profiles/pa/cp42007.PDF 2-31

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report

b. Procedures Gamma Emitter Analysis of Feed: Analysis is performed by scanning a dried, homogenized sample with a gamma spectrometry system. A high resolution germanium detector is utilized with this system. Food samples are loaded into tare weight 300 or 150 ml plastic bottles or 1-liter Marinelli containers, weighed and the net weight of the sample is determined prior to scanning for gamma emitters.

Iodine-13 1 Analysis of Food Crops: Analysis is performed by radiochemistry. A stable iodide carrier is added to a chopped sample, which is then leached with a sodium hydroxide solution, evaporated to dryness and fused in a muffle furnace. The melt is dissolved in water, filtered and treated with sodium hypochlorite. The iodate is then reduced to iodine with hydroxylamine hydrochloride and is extracted into toluene. It is then back-extracted as iodide into sodium bisulfite solution and is precipitated as palladium iodide. The precipitate is weighed for chemical yield and is mounted on a nylon planchet for low level beta counting.

2-32

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report

3. Results and Conclusions A summary of the analysis results during the report period are listed in Table 2-2. A trend graph of analyses (including the pre-operational period through the report period) is shown on Figure 2-7.

a. Feed A total of twelve (12) samples were analyzed by gamma spectrometry. Naturally occurring Potassium40 was identified in twelve of twelve (12 of 12) samples. Naturally occurring Beryllium-7 was found in (6 of 12) samples.

b. Food A total of four (4) samples were analyzed for Iodine-1 31. No detectable concentrations were present.

A total of four (4) samples were analyzed by gamma spectrometry. Naturally occurring Potassium-40 was present in four of four (4 of 4) samples. No other radionuclides were 4ientified.

c. The data from food and feed analyses were consistent with previous data. Based on the analytical results, the operation of the Beaver Valley Power Station did not contribute any measurable increase in radioactivity in the foods and feeds in the vicinity of the site during the report period.

2-33

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Figure 2-6 Environmental Monitoring Locations - Feed Crop and Food Product Sample Site Distance Type No. Sector (miles) Sample Point Description Feed 25 10 2.1 Hookstown, PA (Searight Farm) 10a 3 1.0 Shippingport, PA Food 15a 14 3.7 Georgetown, PA 46a 3 2.5 Industry, PA 48a 10 16.3 Weirton, WV 2-34

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Figure 2-7 Graph of Annual Average Concentration: Cesium-137 in Feed and Food Beaver Valley Power Station REM P Cs-137 Feed and Food Product Trends 100

Cs-137 (Feed)

- - Cs-1 37 (Food)

Cs-137 Pre-operational Results 10-- - - - -- - - -- - - - - -- - -- - - - Cs-137 Required LLD(80 pCQkg) Wet - - - - - _ -- - - -- -

- lb Peporting Level for Feed of Food E

.2 0.1 - -- *---- *-- -- e- - *--

0.01 Urp e 2-35 U

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report E. Monitoring of Local Cow and Goat Milk

1. Description - Milch Animal Locations Samples of fresh milk are obtained from milch animals at locations and frequencies noted in Table 2-1. The milk is analyzed for its radioiodine content, gamma emitters, strontium-89 and strontium-90.

Detailed field surveys are performed during the grazing season to locate and enumerate milch animals within a five (5) mile radius of the site. Survey data for the most recent survey conducted is shown in Section 3, Land Use Census.

2. Sampling Program and Analytical Techniques

a. Program Milk was collected from two (2) reference dairy farms within a 10-mile radius of the BVPS site (Searight Farm and Brunton Farm), and from one (1) control location outside of the 10-mile radius (Windsheimer Farm). Additional dairies, which represent the highest potential milk pathway for radioiodine based on milch animal surveys and meteorological data, were selected and sampled. These dairies are subject to change based upon availability of milk or when more recent data (milch animal census) indicate other locations are more appropriate. The location of each is shown in Figure 2-8 and described below.

2-36

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Approximate Direction and Distance Collection Site Dairy Number of Animals from Midpoint of Unit 1 Period i being Milked Reactor 25 Searight 40 Cows 2.097 miles SSW Jan. - Dec.

27 Brunton 93 Cows 6.158 miles SE Jan. - Dec.

69* Collins 4 Goats 3.547 miles SE Mar. - Oct.

96 Windsheimer 72 Cows 10.476 miles SSW Jan. - Dec.

113* Halstead 64 Cows 5.097 miles SSW Aug. - Dec.

114 Moore 9 Goats 2.120 miles SW Mar. - Dec.

Highest potential pathway dairies The sample from the Searight Farm is collected and analyzed weekly for Iodine-131 using a method that ensures a high sensitivity. Samples from each of the other selected dairies are collected monthly when cows are indoors, and bi-weekly when cows are grazing. The monthly and/or bi-weekly sample is analyzed for Strontium-89, Strontium-90, gamma emitters (including Cesium-137) by high resolution germanium gamma spectranetry and Iodine-131 high sensitivity analysis.

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Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report

b. Procedure Iodine-131 Analysis of Milk: The milk samples are chemically prepared, and then analyzed with a low-level beta counting system.

Gamma Emitter Analysis of Milk: This is determined by gamma spectrometry analysis of a 1 liter Marinelli container of milk.

Strontium-90 Analysis of Milk: The milk samples are prepared by adding a stable strontium carrier and evaporating to dryness, then ashing in a muffle furnace, followed by precipitating phosphates. Strontium is purified in all samples by the Argonne method using 3 grams of extraction material in a chromatographic column. Stable yttrium carrier is added and the sample is allowed to stand for a minimum of 5 days for the in-growth of yttrium-90 (Y-90). Yttrium is then precipitated as hydroxide, is dissolved and re-precipitated as oxalate. The yttrium oxalate is mounted on a nylon planchet and is counted in a low-level beta counter to infer Strontium-90 activity.

Strontium-89 AnaIysis of Milk: The Strontium-89 activity is determined by precipitating strontium carbonate (SrCO 3 ) from the sample after yttrium separation. This precipitate is mounted on a nylon planchet, and is covered with an 80 mg/cm2 aluminum absorber for low level beta counting. Chemical yields of strontium and yttrium are determined by gravimetric means.

3. Results and Conclusions A summary of the analysis results during the report period are listed in Table 2-2. A trend graph of analyses (including the pre-operational period through the report period) is shown on Figure 2-9.

a. A total of one-hundred-sixteen (116) samples were analyzed for Strontium-89 and Strontium-90. Strontium-90 was detected in one-hundred-ten (110) samples at levels attributable to previous nuclear weapons tests and are within the normally expected range.

b. A total of one one-hundred-sixteen (116) samples were analyzed by gamma spectrometry. Naturally occurring Potassium-40 was present in all samples. No other radionuclides were identified.

c. A total of one-hundred forty-eight (148) samples were analyzed for Iodine-131 during the report period. All analyses were less than the 0.5 pico Curie / liter LLD value.

d. Based on all the analytical results and the above investigation, the operation of the Beaver Valley Power Station did not contribute any measurable increase in radioactivity in the milk in the vicinity of the site during the report period.

2-38

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Figure 2-8 Environmental Monitoring Locations - Milk Site Distance Sample Type No. Sector (miles) Sample Point Description 25 10 2.1 Hookstown, PA (Searight Farm) 27 7 6.2 Aliquippa, PA (Brunton Farm)

Milk 69* 7 3.5 Aliquippa, PA (Collins Farm) 96 10 10.5 Burgettstown, PA (Windsheimer Farm) 113* 10 5.1 Hookstown, PA (Halstead Farm) 1141 11 2.1 Hookstown, PA (Moore Farm)

Dairies selected based on highest deposition factors.

2-39

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Figure 2-9 Graph of Annual Average Concentration: Iodine-131 in Milk Beaver Valley Power Stafion REMP 1-131 Concentrations in Milk 14.0 4

12.-ernobyl Acci0et 10.0 - Tes-ng- l- -1970's-ons 3.0 --- s Average at the Idicator Location

. lA..- . Control Location D 1P3I:Re-Operational value (0.6 pC / liter)

, 6.0- t - Required LLD (1 pQi / liter) 0 - Reporting Level (3pi / iter) ffi 4.0 -- - -- - - - -- - - - - ---------

2.0 0.0 - -------------- ---- ---- ------------ ----------------

L oe ^.0le. .0.* , .. -- - -. , :--,

2-40

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report F. Environmental Radiation Monitoring

1. Description of Regional Background Radiation and Sources The terrain in the vicinity of the Beaver Valley Power Station generally consists of rough hills with altitude variations of 300-400 feet. Most of the land is wooded.

The principal geologic features of the region are nearly flat-laying sedimentary beds of the Pennsylvania Age. Beds of limestone alternate with sandstone and shale with abundant interbedded coal layers. Pleistocene glacial deposits partially cover the older sedimentary deposits in the northwest. Most of the region is underlain by shale, sandstone, and some coal beds of the Conemaugh Formation. Outcrops of sandstone, shale, and limestone of the Allegheny Formation exist within the Ohio River Valley and along major tributary streams.

Based on surveys reported in previous annual reports, exposure rates ranged from 6-12 pR/hr.

2. Locations and Analytical Procedures Ambient external radiation levels around the site were measured using thermoluminescent dosimeters (TLDs).

During the report period, there were a total of forty-four (44) offsite environmental TLD locations. The locations of the ILDs are shown in Figure 2-10.

An additional nineteen (19) TLDs were located at selected areas around the fenced perimeter of BVPS. These TLDs (Site No. 33-44,52-56B, 111 and 112) are not plotted on Figure 2-10.

The TLDs were annealed at the Contractor Central Laboratory shortly before placing the TLDs in their field locations. The radiation dose accumulated in-transit between the Central Laboratory, the field location, and the Central Laboratory was corrected by transit controls maintained in lead shields at both the Central Laboratory and the field office. All dosimeters were exposed in the field in a special environmental holder.

3. Results and Conclusions A summary of the TLD results during the report period are listed in Table 2-2. A trend graph of analyses (including the pre-operational period through the report period) is shown on Figure 2-11.

The annual exposure rate of all offsite TLDs averaged 8.4 mR/quarter (0.202 mR/day) during the report period. As in previous years, there was some variation among locations and seasons as would be expected. During the report period, ionizing radiation dose determinations from TLDs averaged 73.6 mR for the year. This is comparable to previous years. There was no evidence of anomalies that could be attributed to the operation of the Beaver Valley Power Station. The TLDs confirm that changes from natural radiation levels, if any, are negligible.

2-41

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Figure 2-10 Environmental Monitoring Locations - TLDs 2-42

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Figure 2-10 (Continued)

TLD Locations SOUTHEAST QUADRANT site Sector Distance Location Site Sctor Distance Location No.. (miles) No. Setr (mie) _ _ _ _ _ _ _ _ _ _ _ _

27 7 6.1 Aliquippa, PA (Brunton Farm) 78 7 2.7 Raccoon Township, PA (Municipal Bldg)

45. 6 1.9 Raccoon Township, PA (Kennedy's Corners) 79 8 4.4 106 Rt 151 - Ted 1 i McWilliams Auto Body 51 5 8.0 Aliquippa, PA (Sheffield Substation) 80 9 8.2 Raccoon Township, PA

._._._ (Park Office, Rt. 18) 59 6 1.0 236 Green Hill Rd. 82 9 6.9 2697 Rt 18 76 5 4.1 Raccoon Township, PA (Elementary School) 94 10 2.3 Hookstown, PA (832 McCleary Rd.)

77 6 5.6 Aliquippa, PA (3614 Green Garden Rd.)

NORTHWEST QUADRANT St Sector Distance Location Setor cSite DistanceLocation No. ( ie)No. (miles) __ _ _ _ _ _ __ _ _ _ _ _

15 14 3.7 Georgetown, PA 87 14 7.0 50103 Calcutta Smith's (Post Office) Ferry Rd.

32 15 0.8 Midland, PA 88 15 2.8 Midland, PA (North Substation) 110

( Summit Roud) 47 14 4.9 East Liverpool, OH 89 15 4.8 Ohioville, PA (Water Department) _ (488 Smith Ferry Road) 60 13 2.5 Georgetown, PA 90 16 5.2 Midland, PA (444 Hill Rd.) (6286 Tuscarawras Road) 86 13 6.2 East Liverpool, OH 93 16 1.1 Midland, PA (1090 Ohio Avenue)

._ (104 Linden - Sunrise Hills)

NORTHEAST QUADRANT Site Sector Distance Location site Sector Distance Location No. (ie) _________________________ No. ____ (miles)I 10 3 1.0 Shippingport, PA 70 1 3.4 Industry, PA (Post Office) (236 Engle Rd.)

28 1 8.60 Sherman Farm 71 2 6.0 Brighton Township (First Western Bank) 29B 3 8.0 Beaver, PA 72 3 3.3 Ohioview, PA

_ _(Friendship Ridge) (Luthem Church- Rear) 30 4 0.5 Shippingport. PA 73 4 2.5 618 Squirrel Run Rd.

(Cook's Ferrv S.S.)

45: 5 2.2 Raccoon Township, PA Christian House Baptist 74 4 7.0 Monaca, PA

, Chapel -Rt. 18) (137 Poplar Ave.- CCBC) 46 3 2.5 Industry, PA (Midway Drive) 75 6 3.8 Aliquippa, PA I(I ?17Holt Road) 6 3 2.3 Industry, PA 91 2 3.9 Pine Grove Rd. & Doyle Rd.

I l (McKeel's Service- Rt. 68) _

l ___ ____ SOUTH WEST QUADRANT Site Distance Location Site Sector Distance Sector Nn. Location No. ftmieles) 131 11 1.4 Hookstown. PA 84 11 8.3 Hancock County, WV (Old Meyer Farm) (Senior Center) 14 11 2.5 Hookstown, PA 85 12 5.7 2048 Rt 30 48 10 16.3 Weirton, WV 92 12 2.8 Georgetown, PA (Water Tower, Collier Way) (Georgetown Road Substation) 81 9 3.6 Millcreek United Presby. Church 95 8 2.2 Hookstown, PA (McCleary & Pole Cat Hollow Rds.)

83 10 4.2 735 Mill Creek Road 2-43

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Figure 2-11 Graph of Annual Average Exposure: Direct Radiation in Environment Beaver Valley Power Station REMP Environmental TLD Trends I 0.20 0 .24 - - - - - - - - - - - - - - - - - - - - -- -- - - - _

-A. ,-- -

0.16,i___________________

014 -- Average of 63 Idicator Lcations- -- - - - - -- _-

0.12 - - -v- - Control Location (Weirton VWV) - -- - - - _

rRe-Operational Vakie (0.2 rrrem/ day) le1 ,ll~ ,4b ,e ,

le , ,1 ,9 , ,,

2-44

.5-

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report G. Monitoring of Fish

1. Description During the report period, fish collected for the radiological monitoring program included channel catfish, bullhead catfish, and freshwater drum.

2. Sampling Program and Analytical Techniques

a. Program Fish samples are collected semi-annually in the New Cumberland pool of the Ohio River at the Beaver Valley effluent discharge point and upstream of the Montgomery Dam. The edible portion of each different species caught is analyzed by gamma spectroscopy. Fish sampling locations are shown in Figure 2-12.

b. Procedure A sample is prepared in a standard tare weight 300 ml plastic bottle and scanned for gamma emitting nuclides with gamma spectrometry system which utilizes a high resolution germanium detector.

3. Results and Conclusions A summary of the analysis results during the report period are listed in Table 2-2. A trend graph of analyses (including the pre-operational period through the report period) is shown on Figure 2-13.

A total of eight (8) samples were analyzed by gamma spectroscopy. No gamma emitting radionuclides were detected.

Based on the analytical results, the operation of the Beaver Valley Power Station did not contribute any measurable increase in radioactivity in the Ohio River fish population during the report period.

2-45

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Figure 2-12 Environmental Monitoring Locations - Fish Site Distance Sample Type No. Sector (miles) Sample Point Description 2A 13 0.2 BVIRS Outfall Vicinity Fish 49a 3 5.0 Industry, PA (Upstream Montgomery I____ ___jI___ Dam) 2-46

I Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Figure 2-13 Graph of Annual Average Concentration: Cesium-137 in Fish Beaver Valley Power Station RM Cs-137 Concentrations - Fish 10000.000 1000.000 -- - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -

- 100.000 - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -

---... Cs-137 1000 -- - - -- - - - Control Location - Fvbontgornary Dam - - - - - - - - - - -

a. 0.00Lkit 2Preoperational (0.014 pOi/ gri E 1.00- equired LUD (150 p/n 1.0

-- --- -- - -- - - Repor ting Level (2000 pai/gmr) 0

-C o 0.0100 - - - - - - - - -- - - - - - - - - - - - -- - - -

o 0 6-2-47 1

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report IL Monitoring of Surface, Drnking, Ground Waters and Precipitation

1. Description of Water Sources The Ohio River is the main body of water in the area. It is used by the Beaver Valley Power Station for plant make-up, for the cooling tower and for receiving plant liquid effluents.

Ohio River water is a source of water for some towns both upstream and downstream of the Beaver Valley Power Station site. It is used by several municipalities and industries downstream of the site. The nearest user of the Ohio River as a potable water source is Midland Borough Municipal Water Authority. The intake of the treatment plant is approximately 1.5 miles downstream and on the opposite side of the river. The next downstream user is East Liverpool, Ohio which is approximately 6 miles downstream. The heavy industries in Midland, as well as others downstream use river water for cooling purposes.

Groundwater occurs in large volumes in the gravel terraces which lie along the river, and diminishes considerably in the bedrock underlying the site. Normal well yields in the bedrock are less than 10 gallons per minute (gpm) with occasional wells yielding up to 60 gpm.

In general, the BVPS site experiences cool winters and moderately warm summers with ample annual precipitation evenly distributed throughout the year. The average annual precipitation for the area is 37.85 inches based on 1971 to 2000 data collected at the Pittsburgh International Airport.

2. Sampling and Analytical Techniques

a. Surface (Raw River) Water The sampling program of river water includes three (3) sampling points along the Ohio River. Raw water samples are collected daily at the East Liverpool (Ohio)

Water Treatment Plant [River Mile 41.2], and the made into weekly composite sample. One automatic river water sampler is located at the ATI-Allegheny Ludlam (formerly J&L Steel) river water intake [River Mile 36.2]. The automatic sampler takes a 20-40 ml sample every 15 minutes and samples are collected on a weekly basis. A weekly grab sample is taken upstream of the Montgomery Dam

[River Mile 29.6]. The weekly grab sample and automatic water sample are then made into a monthly composite sample from each location. In addition, a quarterly composite sample is prepared for each sample point.

The weekly grab samples upstream of the Montgomery Dam are analyzed for Iodine-13 1.

The monthly composites are analyzed for gamma emitters. The quarterly composites are analyzed for tritium.

Locations of each sample point are shown in Figure 2-14.

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Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report

b. Drinking Water (Public Supplies)

Drinking water (i.e.; treated water) is collected at both the Midland, PA and East Liverpool, OH Water Treating Plants. An automatic sampler at each location collects 20-40 ml every 20 minutes, and then made into a weekly composite sample. The weekly composite sample from each location is analyzed for Iodine-13 1.

Monthly composites are made from the weekly samples, and are analyzed by gamma spectrometry. Quarterly composites are analyzed fortritium. Locations of each sample point are shown in Figure 2-14.

c. Groundwater Semi-annual grab samples were collected from three (3) locations within four (4) miles of the site (see Figure 2-14). These locations are:

One (1) well in Shippingport, PA One (1) well in Hookstown, PA One (1) well in Georgetown, PA Each ground water sample is analyzed for tritium and by gamma spectranetry.

d. Precipitation Precipitation is collected at Shippingport, PA, East Liverpool, OH, and Weirton, WV; Precipitation, when available, is collected each week and then made into quarterly composite samples. The quarterly composites are analyzed for tritium and gamma emitters. Locations of each sample point are shown in Figure 2-14.

e. Procedures Gamma Analysis of Groundwater: The analysis is performed on water samples by placing one liter of the sample into a Marinelli container and analyzing the sample on a high resolution germanium gamma spectrometry system.

Tritium Analysis of Groundwater: The tritium is determined in water samples by liquid scintillation analysis.

Iodine-131 Analysis of Groundwater: The sample is chemically prepared, and analyzed with a low-level beta counting system.

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Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report

3. Results and Conclusions A summary of the analysis results of water samples (surface water, drinking water, ground water and precipitation) during the report period are listed in Table 2-2. A trend graph of analyses (including the pre-operational period through the report period) is shown on Figure 2-15.

a. Surface Water A total of twelve (12) samples were analyzed quarterly for Hydrogen-3 (Tritium).

One of twelve (1 of 12) results was positive. The positive value was below the required LLD for tritium in water. That sample was obtained from the Control location, which is five (5) miles upstream of the BVPS outfall facility. The Control location is not influenced by BVPS operation.

A total of thirty-six (36) samples were analyzed by gamma spectrometry. No radionuclides were detected.

A total of fifty-two (52) samples were analyzed for Iodine-13 1 using radiochemical methods. Positive indications were detected in forty-one of fifty-two (41 of 52) weekly samples. The results were similar to previous years, (current years range =

0.3 to 2.3 pico Curie / liter). The positive results were detected at the Control location, which is five (5) miles upstream (not influenced by BVPS operation).

Identification of Iodine-131 during the report period was most likely due to medical diagnostic and treatment procedures. (Reference CR05-05057-01).

b. Drinking Water A total oftwelve (12) samples were analyzed for Tritium. Two of twelve (2 of 12) results were positive. The highest positive value (233 pico Curies / liter) was well below the required LLD (2,000 pico Curies / liter). One (1) of the positive samples was obtained from the Control location, which is five (5) miles upstream of the BVPS outfall facility. The Control location is not influenced by BVPS operation. The other positive sample was obtained from a downstream location, and that value was similar to the upstream value.

A total of thirty-six (36) samples were analyzed by gamma spectrometry. No gamma-emitting radionuclides were detected.

A total of one hundred-fifty-six (156) samples were analyzed for Iodine-131 using radiochemical methods. Positive indications were detected in ninety-six of one-hundred-fifty six (96 of 156) samples. All of the positive values were below the required LLD (1 pico Curie / liter). The positive results were detected at a downstream location and at the Control location, which is five (5) miles upstream (not influenced by BVPS operation). As previously indicated, identification was not due to BVPS discharges and was most likely due to medical diagnostic and treatment procedures.

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Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report

c. Groundwater A total of six (6) samples were each analyzed for Tritium and by gamma spectrometry. No gamma-emitting radionuclides were detected. All six (6) tritium results were less than LLD.

d. Precipitation A total of twelve (12) samples were analyzed for Tritium and by gamma spectrometry. Three of twelve (3 of 12) positive tritium results detected were within normal levels. No gamma emitting radionuclides were detected.

e. Deviations from required sampling schedule and analysis None

f. Summary The data from water analyses demonstrates that the Beaver Valley Power Station did not contribute a significant increase of radioactivity in the local river, in the drinking water, in the well water, or in the precipitation. The analytical results confirm that the station assessments, prior to authorizing radioactive discharges, are adequate and that the environmental monitoring program is sufficiently sensitive.

2-51

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Figure 2-14 Environmental Monitoring Locations -

Ground Water, Surface Water, Drinking Water and Precipitation Site Distance Sample Type No. Sector (miles) Sample Point Description Drinking 4 15 1.3 Midland, PA (Water Departmen)

Water 5 14 4.9 East Liverpool, OH (Water Department) 2.1 14 1.5 Midland, PA (ATI Allegheny Ludlam)

Surface Water 5 14 4.9 East Liverpool, OH (Water Department) 49a 3 5.0 Industry, PA (Upstream Montgomery Dam) 11 3 0.8 Shippingport, PA Ground Water 14a 11 2.5 Hookstown, PA 15a 14 3.7 Georgetown, PA 30 4 0.5 Shippingport, PA (Cook's Ferry Substation)

Precipitation 47 14 4.9 East Liverpool, OH (Water Department) 48 10 16.3 Weirton WV (Water Tower, Collier Way) 2-52

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Figure 2-15 Graph of Annual Average Concentration: Iodine-131 in Surface Water & Drinking Water Beaver Valley Power Station REMP 1-131 Surface Water & Drinking Water Trends 2.5 2.0

+ Dow n Stream Drinkin Water - Mdband

~x Dow n Stream Drinking Water - East Liverpool o + Control Location - Lp Stream Surface Vrter 1.5 Unit 2 DWReoperational (0.23 pCI liter)

=-Requred LLD(I pOI liter)

_Reporting Level (2pCI iter) 1.0 0

0.0 0.5 IO, I* PAo ,

2-53

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Figure 2-16 Graph of Annual Average Concentration: Tritium in Surface Water Beaver Valley Power Station REMP Tritium Trends - Surface Water 100000

- hIdicator Mean (pa/i)

+ Control Location (pa Ii c 10000 Pre- Operational (300 pCiA) _--------_----_-_ -- _-_-_-_ --_-_-_-_ _-_

-Required LLD (2,000 pCi4,

- Reporting Level Surface Water (30,000 pCi :

.C) 1000 - - --- - -- - - -- - - - - - -- - - - - -- - - - - -- - - - -- - -

0V 0.# .g ,

100_

2-54

-7 Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Figure 2-17 Graph of Annual Average Concentration: Tritium in Ground Water Beaver Valley Power Station REMP Tritium Trends - Ground Water 100000 10000

[ -*- -.

-Control A

kIdlator Mean (pCi Loatio (pCi /-r 1-R-quired

-Reportng Re- Operational (300 pCi/n LLD (2,000 pCi/n Level Ground Water (30,000 pCin 100 0 -_- _ _- -_- -_ - _--

.A-100 ----------------------------------........................... -----------------------

10 . . . . . . . . . . . . . . . . . . . . . .

2-55

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Figure 2-18 Graph of Annual Average Concentration: Tritium in Drinking Water Beaver Valley Power Station REMP Tritium Trends - Drinking Wbter 100000

.. indicator Mean

+ Control Location (pQi/

' _Pre- Operational (300 pCifi) 10000 - RequiredLLD(2,000pCR -- - - - - - - - - - - - - - - - _

-Reporbng Level Drinking Water (20,000 pCiA) 00 2-56 Czct,

Beaver Valley Power Station 2004 Annual Radiological Environmental Operating Report L. Estimates of Radiation Dose to Man

1. Pathways to Man - Calculational Models The radiation doses to man as a result of Beaver Valley operations were calculated for both gaseous and liquid effluent pathways using computer codes for the ARERAS/MIDAS computer system. These computer codes are equivalent to NRC computer codes XOQDOQ2, GASPAR, and LADTAP. Dose factors listed in the Offsite Dose Calculation Manual are used to calculate doses from radioactive noble gases in discharge plumes. Beaver Valley effluent data, based on sample analysis were used as the radionuclide activity input.

All liquid and gaseous effluent radionuclides listed in the Annual Radioactive Effluent Release Report were input as source terms to the computer codes.

All batch and continuous gaseous effluent releases were included in the dose assessment calculations. The release activities are based on laboratory analysis.

Meteorological data collected by the Beaver Valley Power Station Meteorology System was also used as input to the computer codes. Except when more recent or specific data was available, the usage factors were obtained from the BVPS Final Environmental Statements or Regulatory Guide 1.109. The airborne effluent pathways evaluated provided population doses out to 50 miles.

All radioactive liquid effluents are released by batch mode after analysis by gamma spectrometry. Each batch is diluted by cooling tower blowdown water prior to discharge into the Ohio River via the main outfall (River Mile 35.0). The actual data from these analyses are tabulated and used as the radionuclide source term input to the computer code. Except when more recent or specific data was available, the usage factors were obtained from the BVPS Final Environmental Statements or Regulatory Guide 1.109. The liquid effluent pathways evaluated provided population doses out to 50 miles.

2. Results of Calculated Population Dose to Man - Liquid Effluent Releases During the report period, the calculated dose to the entire population (-4 million people) within 50 miles of the plant is presented in Table 2-4 for BVPS liquid effluent releases. Also shown in this table is a comparison to natural radiation exposure.

3. Results of Calculated Population Dose to Man - Gaseous Effluent Releases During the report period, the calculated dose to the entire population (-4 million people) within 50 miles of the plant is presented in Table 2-5 for BVPS airborne effluent releases. Also shown in this table is a comparison to natural radiation exposure. The doses include the contribution of all pathways.

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Beaver Valley Power Station 2004 Annual Radiological Environmental Operating Report

4. Conclusions Based upon the estimated dose to individuals from the natural background radiation exposure in Tables 2-4 and 2-5, the incremental increase in total body dose to the 50-mile population (approximately 4 million people), from the operation of Beaver Valley Power Station - Unit 1 and 2, is less than 0.00003% of the annual background dose.

The calculated doses to the public from the operation of Beaver Valley Power Station -

Unit 1 and 2, are below BVPS annual limits and resulted in only a small incremental dose to that which area residents already received as a result of natural background.

The doses constituted no meaningful risk to the public.

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Beaver Valley Power Station 2004 Annual Radiological Environmental Operating Report Table 2-4 Comparison of Natural Radiation Exposure Versus Calculated Population Dose to Man - Liquid Effluent Releases TYPICAL DOSE TO INDIVIDUALS FROM NATURAL RADIATION EXPOSURE (a)

Ambient Gamma Radiation = 58 millirem / year Radionuclides in Body = 40 millirem / year Global Fallout = < 1 millirem / year Radon = 198 millirem / year Average Individual = 296 millirem / year (Total from all sources shown above)

(a)

National Academy of Sciences, "The Effects on Populations of Exposure to Low Levels of Ionizing Radiation," BEIR Report, 1990 0-50 mile Population Dose from BVPS Liquid Effluent Releases Man-millirem Largest Isotope Contributor Total Dose 942 Tritium Average Dose 0.0002355 Tritium (per Individual)

Comparison of Individual Dose BVPS Liquid Effluent Releases Versus Natural Background Radiation millirem BVPS Liquid Effluent Release Dose 0.0002355 Natural Radiation Exposure 296 2-59

Beaver Valley Power Station 2004 Annual Radiological Environmental Operating Report Table 2-5 Comparison of Natural Background Exposure Versus Calculated Population Dose to Man - Gaseous Effluent Releases TYPICAL DOSE TO INDIVIDUALS FROM NATURAL RADIATION EXPOSURE (a)

Ambient Gamma Radiation - 58 millirem / year Radionuclides in Body = 40 millirem / year Global Fallout = < 1 millirem / year Radon - 198 millirem / year Average Individual 296 millirem / year (Total from all sources shown above)

(b) National Academy of Sciences, "The Effects on Populations of Exposure to Low Levels of Ionizing Radiation," BEIR Report, 1990 0-50 mile Population Dose from BVPS Gaseous Effluent Releases Man-millirem Largest

_______ ____ __ _ ___ ____ ___ Isotope Contrib utor Total 296 Tritium Average 0.0000741 Tritium (per Individual)

Comparison of Individual Dose BVPS Gaseous Effluent Releases Versus Natural Background Radiation millirem BVPS Gaseous Effluent Release Dose 0.0000741 Natural Radiation Exposure 296 2-60

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report SECTION 3 - LAND USE CENSUS A Land Use Census was conducted August 1 through October 1, 2005 to comply with:

Unit 1 and Unit 2 Technical Specification 6.8.6b, Item 1

Offsite Dose Calculation Manual procedure 1/2-ODC-3.03, "Controlsfor RETS and REMP Programs", Attachment R, Control 3.12.2, and Surveillance Requirement 4.12.2.1

BVPS REMP procedure 1/2-ENV-04.02, "Milch Animal Sampling Location Determination& ODCMProcedure1/2-ODC-3.03, Control3.12.2 Action Statements a and b Compliance Determination" The Land Use census indicates that no changes were required in the current sampling locations, and no changes were required to the methodology used for determination of offsite dose from plant releases. A numerical summary of the Land Use Census results are provided in Table 3-1.

The following information is also provided to clarify the Land Use Census results as documented in Condition Report No. CR05-07299:

Nearest Resident:

The current location has not changed since the previous census.

The current location is at 211 Ferry Hill Road, Shippingport, PA (0.406 miles NE).

Nearest Garden >500 saft:

The current location has changed since the previous census.

The previous location was at 158 Morrow Drive, Shippingport, PA (1.028 miles ENE).

The current location is at 238 State Route 168, Hookstown, PA (0.760 miles SSW).

Nearest Dairy Cow Milked:

The current location has not changed since the previous census.

The current location is at Searight Dairy, 948 McCleary Road, RD 1, Hookstown, PA (2.097 miles SSW).

Nearest Doe Goat Milked:

The current location has not changed since the previous census.

The current location is at 982 State Route 168, Hookstown, PA (2.120 miles SW).

NOTE: this is not the nearest location, but it is the nearest location providing samples.

Nearest Beef Cattle:

The current location has not changed since the previous census.

The current location is at 105 Shippingport Road, Shippingport, PA (1.405 miles ENE).

3-1

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report

Projection for 2006 Dairy Cow Sampling Locations:

Using a linear regression analysis of deposition parameters (D/Q), Dairy Cow sampling locations were determined to remain at the same locations used in 2005:

- Searight Dairy, 948 McCleary Road, RDI, Hookstown, PA (2.097 miles SSW)

- Halstead Dairy, 104 Tellish Drive, Hookstown, PA (5.079 miles SSW)

- Brunton Dairy, 3681 Ridge Road, Aliquippa, PA (6.158 miles SE)

- Weindsheimer Dairy, RD 1 Burgettstown, PA (10.476 miles SSW).

Projection for 2006 Doe Goat Sampling Locations:;

The linear regression analysis also indicated that the Doe Goat sampling locations will remain at the same locations used in 2005:

- Moore Farm, 982 State Route 168, Hookstown, PA (2.120 miles SW)

- Collins Farm, 289 Calhoun Road, Aliquippa, PA (3.547 miles, SE).

3-2

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Table 3-1 Location of Nearest Residents, Gardens, Dairy Cows, Doe Goats and Beef Cattle RESIDENT DAIRY DOE BEEF SECTOR S GARDENS COWS GOATS CATTLE 0 to 5 miles 0 to 5 miles 0 to 5 miles 0 to 5 miles 0 to 5 miles (miles) (miles) (miles) (miles) (miles)

N 1.584 2.899 None None 3.461 NNE 1.661 None None None 3.110 NE 0.406 2.711 None None 4.869 ENE 0.598 1.028 None None 1.405 E 0.429 1.979 None 3.402 2.620 ESE 0.476 1.713 None 4.285 2.952 SE 1.583 1.802 None 2.293 1.974 SSE 1.102 2.127 None None 4.573 S 1.399 2.276 3.851 None 2.337 SSW 0.760 0.760 2.097 1.818 1.832 SW 1.453 1.453 None 2.120 1.452 WSW 1.394 2.832 None 3.849 1.544 W 2.204 None 2.701 None 3.176 WNW 2.742 None None None None NW 0.885 1.033 None 5.125 4.277 NNW 0.902 1.353 2.442 None 2.416 NOTE: Distances shown in Bold print are the nearest location for that receptor 3-3

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report SECTION 4 - SPLIT SAMPLE AND SPIKE SAMPLE INTER-LABORATORY COMPARISON PROGRAM A. Split Sample Program (Inter-Laboratory Comparison, Part 1 of 2): BVPS participates in a split sample program with the Pennsylvania Department of Environmental Protection (PADEP) in support of their nuclear power plant monitoring program.

BVPS provided split samples to PADEP throughout the report period. The shared media and number of locations were typically comprised of; milk (1), surface water (3), sediment (1), fish (1), and food crops (2).

PADEP has co-located continuous air particulate & air iodine sample stations with four (4) of the BVPS locations.

PADEP has co-located TLDs with twenty-four (24) of the BVPS TLDs.

B. Spike Sample Program (Inter-Laboratory Comparison, Part 2 of 2): BVPS participates in a spike sample program with an Independent Laboratory. This program is used to independently verify sample analyses performed by the BVPS Contractor Laboratory.

The NRC criteria listed in NRC Inspection Procedure 84750, 12/4/90, Inspection Guidance 84750-03 is used as the acceptance criteria for comparisons of results of spiked samples between the Contractor Lab and the Independent Lab. These comparisons are performed by dividing the comparison standard (Independent Lab result) by its associated uncertainty to obtain the resolution. The comparison standard value is multiplied by the ratio values obtained from the following table to find the acceptance band for the result to be compared.

However, in such cases where the counting precision of the standard yields a resolution of less than 4, a valid comparison is not practical, and therefore, not performed.

Resolution Ratio

<4 4

4-7 - 0.50 - 2.00 -

8- 15 0.60- 1.66 16 - 50 0.75 - 1.33 51 - 200 0.80 - 1.25

> 200 0.85 - 1.18 4-1

- Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Participation in an Inter-Laboratory Comparison Program is required by BVPS Unit 1 and 2 Technical Specification 6.8.6b, Item 3. For the report period, the requirement was met by the Contractor Lab analyzing NIST traceable spiked samples supplied by an Independent Lab.

During the report period, BVPS used (Environmental, Inc., Midwest Laboratory - Northbrook, IL) as the Contractor Laboratory, and (Analytics- Atlanta, GA) as the Independent Laboratory.

The spiked samples included air particulate filter papers, charcoal cartridges, water samples, and milk samples. The samples were submitted by the Independent Laboratory to the Contractor Laboratory for analysis. The "spiked to" values were used for calculating comparison Acceptance Criteria.

Spiked Milk & Water Samples: The spiked sample results for each calendar quarter are reported in Table 4-1 through Table 4-4, respectively. The following summary is provided:

- A total of forty-eight (48) gamma spectrometry radionuclide analyses were performed by the Contractor Laboratory on four (4) milk samples.

- A total of forty-eight (48) gamma spectrometry radionuclide analyses were performed by the Contractor Laboratory on four (4) water samples.

A total of four (4) tritium analyses were performed by the Contractor Laboratory on four (4) water samples.

Comparison of results of the spiked milk and water samples showed acceptable agreement. All one-hundred (100) analyses performed by the Contractor Laboratory were within the Acceptance Criteria.

Spiked Filter Paper and Charcoal Cartridge Samples: The spiked sample results for each calendar quarter are also reported in Table 4-1 through Table 4-4, respectively. The following summary is provided:

- Gross Beta (Cesium-137) analyses were performed by the Contractor Laboratory on two (2) filter paper samples.

- Iodine-1 31 analyses were performed by the Contractor Laboratory on two (2) charcoal cartridge samples.

- Comparison of results of the spiked filter paper and charcoal cartridge samples showed acceptable results. All four (4) analyses performed by the Contractor Laboratory were within the Acceptance Criteria.

4-2

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report B. Conclusions

Results of Sylit Sample Program:

SINCE the split sample program is coordinated by the state, THEN the results are not provided with this report.

Results of Spike Sample Program:

Based on the Inter-Laboratory comparison data, BVPS considers all analyses provided throughout the report period by the Contractor Laboratory to be acceptable with respect to both accuracy and measurement. A comparison of the data is provided in the following tables.

4-3

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Table 4-1 Inter-Laboratory Comparison Program Spiked Samples - lt Quarter Percent Difference Between Sample Type and Contractor Lab Activity and Sample Date Identification No. Sample Analyses Independent Lab Calculated Activity (Contr. Lab - Ind. Lab) I Ind. Lab Sr-89 -6.16%

Sr-90 12.86%

1-131 -1.72%

Ce-141 -5.08%

Cr-51 -6.65%

04/14/2005 041105 Water Ind Lab: E4560-93 Cs-134 Cs-137 ___0_____40

-9.01% ______

Con. Lab: SPW-1852 Co-58 -2.94%

Mn-54 -0.55%

Fe-59 3.43%

Zn-65 -OAO%

Co-60 -2.46%

Water 04/14/2005 Ind. Lab: E4559-93 H-3 7.38%

Con. Lab: SPW-1848 Sr-89 -0.54%

Sr-90 15.56%

1-131 -2.32%

Ce-141 4.87%

Milk Cr-51 14.16%

04/14/2005 Ind. Lab: E4561-93 Cs-134 -6.16%

Con. Lab: SPMI-1849 Cs-1 37 -0.08%

Co-58 -2.22%

Mn-54 0.36%

Fe-59 6.42%

Zn-65 1.18%

Co-60 -5.23%

Filter Paper md. Cs-I 37 04/14/2005 Ind. Lab: E4562-93 11.21%

Con. Lab: SPAP-1850 (Gross Beta)

Charcoal Cartridge 04/14/2005 Ind. Lab: E4563-93 1-131 -4.50%

Con. Lab: SPCH-1851 4-4

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Table 4-2 Inter-Laboratory Comparison Program Spiked Samples - 2 nd Quarter Percent Difference Between Sample Typo and Contractor Lab Activity and Sample Date Identification No. Sample Analyses Independent Lab Calculated Activity (Contr. Lab - Ind. Lab) I Ind. Lab Sr-89 -0.11%

Sr-90 -5.83%

1-131 2.02%

Ce-141 2.67%

Water Cr-51 2.76%

06/09/2005 Ind. Lab: E4595-93 Cs-134 -6.44%

Con. Lab: SPW-3168 Cs-I37 9.51%

Co-58 1.67%

Mn-54 -0.96%

Fe-59 -0.71%

Zn-65 3.02%

Co-60 -4.11%

Water 06/09/2005 Ind. Lab: E4594-93 H-3 -0.74%

Con. Lab: SPW-3166 Sr-89 -0.80%

Sr-90 11.82%

1-131 -1.49%

Ce-141 0.65%

Milk Cr-51 -4.06%

06/09/2005 Ind. Lab: E4596-93 Cs-134 -7.58%

Cs-137 130.26%

Con. Lab: SPMI-3167 Co58 26.00%

Mn-54 -1.04%

Fe-59 0.16%

Zn-65 2.97%

Co-60 -3.72%

4-5

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Table 4-3 Inter-Laboratory Comparison Program Spiked Samples - 3 ir Quarter Percent Difference Between l TContractor Lab Activity and Sample Date Sample TypeianN Sample Analyses Independent Lab Calculated Activity (Contr. Lab - Ind. Lab) I Ind. Lab Sr-89 -1.12%

Sr-90 8.18%

1-131 0.77%

Ce-141 0.53%

Cr-51 -1.32%

09/15/2005 09/15/2005 Water Ind. Lab: E4722-93CsI3 Cs-134 -6.62%

Cs-1370.68%

Con. Lab: SPW-5160 Co-58 6.49%

Mn-54 5.86%

Fe-59 4.19%

Zn-65 2.08%

Co-60 -2.82%

Water 09/15/2005 Ind. Lab: E4721-93 H-3 5.78%

Con. Lab: SPW-5156 Sr-89 -9.32%

Sr-90 5.83%

1-131 -3.83%

Ce-141 -1.76%

Cr-SI -7.87%

Milk Cs-134 -6.64%

09/15/2005 Ind. Lab: E4723-93 Cs-I 37 Cs-137-0.15%

Con. Lab: SPMI-5157 Co-58 -1.43%

Mn-54 3.15%

Fe-59 8.03%

Zn-65 2.11%

Co-60 -4.19%

Filter Paper Cs-137 09/15/2005 Ind. Lab: E4724-93 16.55%

Con. Lab: SPAP-5158 (Gross Beta)

Charcoal Cartridge 09/15/2005 Ind. Lab: E4725-93 1-131 -5.94%

Con. Lab: SPCH-5159 4-6

Beaver Valley Power Station 2005 Annual Radiological Environmental Operating Report Table 4-4 Inter-Laboratory Comparison Program Spiked Samples - 4t Quarter Percent Difference Between Sample Type and Contractor Lab Activity and Sample Date Identification No. Sample Analyses Independent Lab Calculated Activity (Contr. Lab - Ind. Lab) I Ind. Lab Sr-89 0.11%

Sr-90 -2.86%

1-131 1.70%

Ce-141 -1.88%

Cr-51 0.42%

Water Cs-1 34 -6.72%

12/08/2005 Ind. Lab: E4847-93 Cs-I37 Cs-1372.01%

Con. Lab: SPW-6886 Co-58 -2.98%

Mn-54 4.73%

Fe-59 -0.33%

Zn-65 1.06%

Co-60 0.99%

Water 12/08/2005 Ind. Lab: E4846-93 H-3 -1.24%

Con. Lab: SPW-6884 Sr-89 -16.17%

Sr-90 4.00%

1-131 -5.87%

Ce-141 -3.35%

Cr-51-021%

Milk Cs-134 -7.13%

12/08/2005 Ind. Lab: E4848-93 Cs-137 Cs-137-2.06%

Con. Lab: SPMI-6885 Co-58 -0.90%

Mn-54 2.11%

Fe-59 4.39%

Zn-65 4.55%

Co-60 -3.24%

4-7

L-06-079, Annual Radioactive Effluent Release Report for 2005, and Annual Radiological Environmental Operating Report for 2005

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L-06-079, Annual Radioactive Effluent Release Report for 2005, and Annual Radiological Environmental Operating Report for 2005

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