Text

Annual Radiological Environmental Operating Report
	ML061420402
Person / Time
Site:	Quad Cities
Issue date:	05/12/2006
From:	Tulon T; Exelon Generation Co, Exelon Nuclear
To:	; Document Control Desk, Office of Nuclear Reactor Regulation
References
	FOIA/PA-2010-0209, SVP-06-048
	Download: ML061420402 (209)
	v • d • e

Exelkn.

Exelon Generation Company, LLC www.exeloncorp.com Nuclear Ouad Cities Nuclear Power Station 22710 206"h Avenue North Cordova, IL 61242-9740 SVP-06-048 May 12, 2006 U. S. Nuclear Regulatory Commission ATTN: Document Control Desk Washington, D.C. 20555 Quad Cities Nuclear Power Station, Units I and 2 Renewed Facility Operating License Nos. DPR-29 and DPR-30 NRC Docket Nos. 50-254 and 50-265

Subject:

Quad Cities Nuclear Power Station Annual Radiological Environmental Operating Report In accordance with Quad Cities Technical Specifications 5.6.2, enclosed is the 2005 Radiological Environmental Operating Report for Quad Cities Nuclear Power Station.

This report contains the results of the radiological environmental and meteorological monitoring programs.

Should you have any questions concerning this letter, please contact Mr. W. J. Beck at (309) 227-2800.

Respectfully, T ~ty J.Tuo RieVice President Quad Cities Nuclear Power Station

Attachment:

The Quad Cities Nuclear Power Station 2005 Annual Radiological Environmental Operating Report cc: Regional Administrator - NRC Region IlIl NRC Senior Resident Inspector- Quad Cities Nuclear Power Station vE2-

May 12, 2006 U.S. Nuclear Regulatory Commission Page 2 bcc: NRC Project Manager - NRR Illinois Emergency Management Agency - Department of Nuclear Safety Senior Reactor Analyst - NRC Region IlIl Manager of Energy Practice - Winston and Strawn Director, Licensing and Regulatory Affairs - Cantera Manager, Licensing, Dresden and Quad Cities Stations Exelon Document Control Desk Licensing (Hard Copy)

Exelon Document Control Desk Licensing (Electronic Copy)

J. Gust - MidAmerican Energy Company D. Tubbs - MidAmerican Energy Company Regulatory Assurance Manager - Dresden Nuclear Power Station Regulatory Assurance Manager - Quad Cities Nuclear Power Station NRC Coordinator - Quad Cities Nuclear Power Station NSRB Site Coordinator - Quad Cities Nuclear Power Station INPO Site Coordinator - Quad Cities Nuclear Power Station (no attachments)

INPO Records Center SVP Letter File American Nuclear Insurers Library Frank Niziolek - Illinois Department of Nuclear Safety Environmental Law & Policy Center, Financial Analyst US Environmental Protection Agency, Air & Radiation Division, Region V Ellen Saar - Environmental, Inc. Midwest Laboratory Lynne Perry - Teledyne-Browne Engineering Inc.

ODCM Coordinator - Cantera Murray and Trettel, Inc.

Ken Ohr, Radiation Protection Manager - Quad Cities Station Scott Kirkland, ODCM Chemist - Quad Cities Station Vicki Neels, Chemistry Manager - Quad Cities Station Paul Behrens, Nuclear Oversite - Quad Cities Station Chemistry Clerk - Quad Cities Station

Attachment Quad Cities Nuclear Power Station 2005 Annual Radiological Environmental Operating Report

Docket No: 50-254 50-265 QUAD CITIES NUCLEAR POWER STATION UNITS I and 2 Annual Radiological Environmental Operating Report 1 January Through 31 December 2005 Prepared By Teledyne Brown Engineering Environmental Services

__ SM Nuclear Quad Cities Nuclear Power Station Cordova, IL 61242 May 2006

Table Of Contents

1. Summary and Conclusions ... 1.......................

II. Introduction........................................................................................................................2 A. Objectives of the REMP ............................. 2 B. Implementation of the Objectives .............................. 2 Il. Program Description .............................. 2 A. Sample Collection .............................. 2 B. Sample Analysis ... 4.......................

C. Data Interpretation .............................. 5 D. Program Exceptions ............................... 7 E. Program Changes ............................. 9 IV. Results and Discussion . . .............................. 10 A. Aquatic Environment . . . ........................... 10

1. Surface Water ..... 10

2. Ground Water ..... 10

3. Fish .............................. 11

4. Sediment ..... 11 B. Atmospheric Environment ............................. 11

1. Airborne ........................ 11

a. Air Particulates ............................. 11

b. Airborne Iodine.............................................................................. 12

2. Terrestrial ..... 13

a. Milk ............................. 13

b. Food Products ............................. 13 C. Ambient Gamma Radiation . . . . 13 D. Interim Spent Fuel Storage . . . . 14 E. Land Use Survey .... 14 F. Errata Data ..................... 15 G. Summary of Results - Inter-laboratory Comparison Program ........................... 16 2 of 206

Appendices Appendix A Radiological Environmental Monitoring Report Summary Tables Table A-1 Radiological Environmental Monitoring Program for Quad Cities Nuclear Power Station, 2005 Appendix B Location Designation, Distance & Direction, and Sample Collection &

Analytical Methods TabIes Table B-1: Radiological Environmental Monitoring Program - Sampling Locations, Distance and Direction, Quad Cities Nuclear Power Station, 2005 Table B-2: Radiological Environmental Monitoring Program - Summary of Sample Collection and Analytical Methods, Quad Cities Nuclear Power Station, 2005 Figures Figure B-1: Quad Cities Outer Ring TLDs and Air Sampling Sites, 2005 Figure B-2: Quad Cities Inner Ring TLD Locations, 2005 Figure B-3: Quad Cities Milk, Fish, Water and Sediment Sampling Locations, 2005 Appendix C Data Tables and Figures - Primary Laboratory Tables Table C-1.1 Concentrations of Gross Beta in Surface Water Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.

Table C-1.2 Concentrations of Tritium in Surface Water Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.

Table C-1.3 Concentrations of Gamma Emitters in Surface Water Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.

Table C-11.1 Concentrations of Tritium in Ground Water Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.

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Table C-11.2 Concentrations of Gamma Emitters in Ground Water Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.

Table C-111.1 Concentrations of Gamma Emitters in Fish Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.

Table C-IV.1 Concentrations of Gamma Emitters in Sediment Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.

Table C-V.1 Concentrations of Gross Beta in Air Particulate Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.

Table C-V.2 Monthly and Yearly Mean Values of Gross Beta Concentrations (E-3 pCi/cu meter) in Air Particulate Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.

Table C-V.3 Concentrations of Gamma Emitters in Air Particulate Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.

Table C-VI.1 Concentrations of 1-131 in Air Iodine Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.

Table C-VII.1 Concentrations of 1-131 in Milk Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.

Table C-VII.2 Concentrations of Gamma Emitters in Milk Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.

Table C-VIII.1 Concentrations of Gamma Emitters in Food Products Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.

Table C-IX.1 Quarterly TLD Results for Quad Cities Nuclear Power Station, 2005.

Table C-IX.2 Mean Quarterly TLD Results for the Inner Ring, Outer Ring, Other and Control Locations for Quad Cities Nuclear Power Station, 2005.

Table C-IX.3 Summary of the Ambient Dosimetry Program for Quad Cities Nuclear Power Station, 2005.

Table C-X.1 Summary of Collection Dates for Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.

Eigures Figure C-1 Surface Water - Gross Beta - Stations Q-33 and Q-34 (C) Collected in the Vicinity of QCNPS, 2000 - 2005.

Figure C-2 Surface Water - Tritium - Stations Q-33 and Q-34 (C) Collected in the Vicinity of QCNPS, 2000 - 2005.

Figure C-3 Ground Water - Tritium - Station Q-35 and Q-36 Collected in the Vicinity of QCNPS, 2000 - 2005.

Figure C-4 Air Particulates - Gross Beta - Stations Q-01 and Q-02 Collected in the Vicinity of QCNPS, 2000 - 2005.

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Figure C-5 Air Particulates - Gross Beta - Stations Q-03 and Q-04 Collected in the Vicinity of QCNPS, 2000 - 2005.

Figure C-6 Air Particulates - Gross Beta - Station Q-07 (C) Collected in the Vicinity of QCNPS, 2000 - 2005.

Figure C-7 Air Particulates - Gross Beta - Stations Q-1 3 and Q-1 6 Collected in the Vicinity of QCNPS, 2005.

Figure C-8 Air Particulates - Gross Beta - Stations Q-37 and Q-38 Collected in the Vicinity of QCNPS, 2005.

Appendix D Inter-Laboratory Comparison Program Tablps Table D-1 Analytics Environmental Radioactivity Cross Check Program Teledyne Brown Engineering, 2005 Table D-2 ERA Environmental Radioactivity Cross Check Program Teledyne Brown Engineering, 2005 Table D-3 DOE's Mixed Analyte Performance Evaluation Program (MAPEP)

Teledyne Brown Engineering, 2005 Table D-4 ERA Statistical Summary Proficiency Testing Program Environmental, Inc., 2005 Table D-5 DOE's Mixed Analyte Performance Evaluation Program (MAPEP)

Environmental, Inc., 2005 Appendix E Errata Data Appendix F Effluent Data Appendix G Meteorological Data iv 5 of 206

I. Summary and Conclusions This report on the Radiological Environmental Monitoring Program (REMP) conducted for the Quad Cities Nuclear Power Station (QCNPS) by Exelon covers the period 1 January 2005 through 31 December 2005. During that time period, 1,013 analyses were performed on 928 samples. In assessing all the data gathered for this report and comparing these results with preoperational data, it was concluded that the operation of QCNPS had no adverse radiological impact on the environment.

Surface water samples were analyzed for concentrations of gross beta, tritium and gamma emitting nuclides. Ground water samples were analyzed for concentrations of tritium and gamma emitting nuclides. No fission or activation products were detected. Gross beta and tritium activities detected were consistent with those detected in previous years and consistent with the control stations.

Fish (commercially and recreationally important species) and sediment samples were analyzed for concentrations of gamma emitting nuclides. No fission or activation products were detected in fish. Sediment samples contained Cesium-137 concentrations consistent with levels observed during the preoperational years. No fission products or activation products resulting from plant operations were found in sediment.

Air particulate samples were analyzed for concentrations of gross beta and gamma emitting nuclides. No fission or activation products were detected.

High sensitivity 1-131 analyses were performed on air samples. No 1-131 was detected.

Cow milk samples were analyzed for concentrations of 1-131 and gamma emitting nuclides. No 1-131 was detected. Concentrations of naturally occurring K-40 were consistent with those detected in previous years. No fission or activation products were detected.

Food product samples were analyzed for concentrations of gamma emitting nuclides. No fission or activation products were detected.

Environmental gamma radiation measurements were performed quarterly using thermoluminescent dosimeters. Levels detected were consistent with those observed in previous years.

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II. Introduction The Quad Cities Nuclear Power Station (QCNPS), consisting of two 2957 MWth boiling water reactor owned and operated by Exelon Corporation, is located in Cordova, Illinois along the Mississippi River. Unit No. 1 went critical on 16 March 1972. Unit No. 2 went critical on 02 December 1973. The site is located in northern Illinois, approximately 182 miles west of Chicago, Illinois.

This report covers those analyses performed by Teledyne Brown Engineering (TBE), Global Dosimetry, and Environmental Inc. (Midwest Labs) on samples collected during the period 1 January 2005 through 31 December 2005.

A. Objective of the REMP The objectives of the REMP are to:

1. Provide data on measurable levels of radiation and radioactive materials in the site environs.

2. Evaluate the relationship between quantities of radioactive material released from the plant and resultant radiation doses to individuals from principal pathways of exposure.

B. Implementation of the Objectives The implementation of the objectives is accomplished by:

1. Identifying significant exposure pathways.

2. Establishing baseline radiological data of media within those pathways.

3. Continuously monitoring those media before and during Station operation to assess Station radiological effects (if any) on man and the environment.

Ill. Program Description A. Sample Collection Samples for the QCNPS REMP were collected for Exelon Nuclear by Environmental Inc. (Midwest Labs). This section describes the general sampling methods used by Environmental Inc. to obtain environmental 7 of 206

samples for the QCNPS REMP in 2005. Sample locations and descriptions can be found in Table B-1 and Figures B-1 through B-3, Appendix B.

Aquatic Environment The aquatic environment was evaluated by performing radiological analyses on samples of surface water, ground water, fish, and sediment.

Surface water samples were collected weekly from two locations, Q-33 and Q-34 (C). Ground water samples were collected quarterly from two locations, Q-35 and Q-36. All water samples were collected in new containers, which were rinsed with source water prior to collection.

Fish samples comprising the edible portions of commercially and recreationally important species were collected semiannually at two locations, Q-24 and Q-29 (Control). Sediment samples composed of recently deposited substrate were collected at one location semiannually, Q-39.

Atmospheric Environment The atmospheric environment was evaluated by performing radiological analyses on samples of air particulate, airborne iodine, and milk. Airborne iodine and particulate samples were collected and analyzed at nine locations (Q-01, Q-02, Q-03, Q-04, Q-07, Q-13, Q-16, Q-37 and Q-38).

The control location was Q-07. Airborne iodine and particulate samples were obtained at each location, using a vacuum pump with charcoal and glass fiber filters attached. The pumps were run continuously and sampled air at the rate of approximately one cubic foot per minute. The air particulate filters were replaced weekly and sent to the laboratory for analysis. The air iodine samples were replaced biweekly and sent to the laboratory for analysis.

Milk samples were collected biweekly at one location (Q-26) from May through October, and monthly from November through April. All samples were collected in new plastic containers from the bulk tank, preserved with sodium bisulfite, and shipped promptly to the laboratory.

Food products were collected annually in July at five locations (Q-Quad 1 Control, Q-Quad 1, Q-Quad 2, Q-Quad 3, and Q-Quad 4). The control location was Q-Quad I - Control. Various types of broadleaf and root vegetables were collected and placed in new plastic bags, and sent to the laboratory for analysis.

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Ambient Gamma Radiation Direct radiation measurements were made using thermoluminescent dosimeters (TLD). Each location consisted of 2 TLD sets. The TLD locations were placed on and around the QCNPS site as follows:

An inner ring consisting of 15 locations (Q-101, Q-102, Q-103, Q-104, Q-105, Q-106, Q-107, Q-108, Q-109, Q-111, Q-112, Q-113, Q-114, Q-115 and Q-116). These TLD are located in 15 of the 16 meteorological sectors in the general area of the site boundry (approximately 0.1 - 3 miles from the site). There are no TLDs located in the SSW sector because this sector is located over water.

An outer ruing consisting of 16 locations (Q-201, Q-202, Q-203, Q-204, Q-205, Q-206, Q-207, Q-208, Q-209, Q-210, Q-211, Q-212, Q-213, Q-214, Q-215 and Q-216). These TLDs are located in each of the 16 meteorological sectors (approximately 3.7 - 5 miles from the site)

An ather set consisting of eight locations (Q-01, Q-02, Q-03, Q-04, Q-13, Q-16, Q-37 and Q-38. The locations are at each of the air sample stations around the site.

The balance of one location (Q-07) is the control site.

The specific TLD locations were determined by the following criteria:

1. The presence of relatively dense population;

2. Site meteorological data taking into account distance and elevation for each of the sixteen-22 1/2 degree sectors around the site, where estimated annual dose from QCNPS, if any, would be most significant;

3. On hills free from local obstructions and within sight of the stack (where practical);

4. And near the closest dwelling to the stack in the prevailing downwind direction.

The TLDs were exchanged quarterly and sent to Global Dosimetry for analysis.

B. Sample Analysis This section describes the general analytical methodologies used by TBE 9 of 206

and Environmental Inc. (Midwest Labs) to analyze the environmental samples for radioactivity for the QCNPS REMP in 2005 and the type of analyses. The analytical procedures used by the laboratories are listed in Table B-2.

In order to achieve the stated objectives, the current program includes the following analyses:

1. Concentrations of beta emitters in surface water and air particulates.

2. Concentrations of gamma emitters in ground and surface water, air particulates, milk, fish, sediment and vegetation.

3. Concentrations of tritium in ground and surface water.

4. Concentrations of 1-131 in air and milk.

5. Ambient gamma radiation levels at various site environs.

C. Data Interpretation The radiological and direct radiation data collected prior to Quad Cities Nuclear Power Station becoming operational were used as a baseline with which these operational data were compared. For the purpose of this report, Quad Cities Nuclear Power Station was considered operational at initial criticality. In addition, data were compared to previous years' operational data for consistency and trending. Several factors were important in the interpretation of the data:

1. Lower Limit of Detection and Minimum Detectable Concentration The lower limit of detection (LLD) was defined as the smallest concentration of radioactive material in a sample that would yield a net count (above background) that would be detected with only a 5% probability of falsely concluding that a blank observation represents a "real" signal. The LLD was intended as an a priori (a before the fact) estimate of a system (including instrumentation, procedure and sample type) and not as an a posteriori (after the fact) criteria for the presence of activity. All analyses were designed to achieve the required QCNPS detection capabilities for environmental sample analysis.

The minimum detectable concentration (MDC) is defined above with the exception that the measurement is an a posteriori (after the 10 of 206

fact) estimate of the presence of activity.

2. Net Activity Calculation and Reporting of Results Net activity for a sample was calculated by subtracting background activity from the sample activity. Since the REMP measures extremely small changes in radioactivity in the environment, background variations may result in sample activity being lower than the background activity effecting a negative number. An MDC was reported in all cases where positive activity was not detected.

Gamma spectroscopy results for each type of sample were grouped as follows:

For surface water 12 nuclides, Mn-54, Co-58, Fe-59, Co-60, Zn-65, Zr-95, Nb-95,1-131, Cs-134, Cs-137, Ba-140, and La-140 were reported.

For ground water 11 nuclides, Mn-54, Co-58, Fe-59, Co-60, Zn-65, Zr-95, Nb-95, Cs-134, Cs-137, Ba-140, and La-140 were reported.

For fish nine nuclides, Mn-54, Co-58, Fe-59, Co-60, Zn-65, Nb/Zr-95, Cs-134, Cs-137 and Ba/La-140 were reported.

For sediment nine nuclides, Mn-54, Co-58, Fe-59, Co-60, Zn-95, Nb/Zr-95, Cs-134, Cs-137 and Ba/La-140 were reported.

For air particulate nine nuclides, Mn-54, Co-58, Fe-59, Co-60, Zn-65, Nb/Zr-95, Cs-134, Cs-137 and Ba/La-140 were reported.

For milk 10 nuclides, Mn-54, Co-58, Fe-59, Co-60, Zn-65, Nb/Zr-95, Cs-134, Cs-137, Ba-140 and La-140 were reported.

For vegetation 10 nuclides, Mn-54, Co-58, Fe-59, Co-60, Zn-65, Nb/Zr-95,1-131, Cs-1 34, Cs-1 37 and Ba/La-140 were reported.

Means and standard deviations of the results were calculated. The standard deviations represent the variability of measured results for different samples rather than single analysis uncertainty.

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D. Program Exceptions For 2005 the QCNPS REMP had a sample recovery rate in excess of 99%. Sample anomalies and missed samples are listed in the tables below:

Table D-1 LISTING OF SAMPLE ANOMALIES Sample Location Collection Reason TvDe Code Date A/I Q-03 07/02/05 Collector removed bird's nest from intake pipe; nest was not blocking flow. Bird may have pecked filter.

A Q-03 07/08/05 Collector removed bird's nest from intake pipe; nest was not blocking flow. Bird may have pecked filter.

A/I Q-01 07/15/05 Filter paper stuck to sampling train; slightly torn.

A Q-07 08/19/05 Low reading of 163.0 hours0 days 0 hours 0 weeks 0 months due to pump burn out; collector replaced pump.

A/l Q-02 08/26/05 Low reading of 13.1 hours1.157407e-5 days 2.777778e-4 hours 1.653439e-6 weeks 3.805e-7 months due to faulty surge protector; collector replaced surge protector.

A Q-02 09/02/05 Low meter reading of 143.3 hours3.472222e-5 days 8.333333e-4 hours 4.960317e-6 weeks 1.1415e-6 months due to replacement of malfunctioning surge protector.

A/l Q-01 10/07/05 Low timer reading of 119.4 hours4.62963e-5 days 0.00111 hours 6.613757e-6 weeks 1.522e-6 months due to power outage; Station Point of Contact notified; estimated flowrate of 62 CFH used for COCs to Teledyne.

A Q-13 10/14/05 Low reading of 159.5 hours5.787037e-5 days 0.00139 hours 8.267196e-6 weeks 1.9025e-6 months due to work being done at substation.

A Q-01 10/28/05 Low reading of 71.7 hours8.101852e-5 days 0.00194 hours 1.157407e-5 weeks 2.6635e-6 months due to power outage; power restored on 10/25/05 at 12:00 p.m. Collector field checked pump.

A Q-07 11/25/05 Low vacuum of 16 inches Hg due to pump malfunction; collector replaced pump.

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Table D-2 LISTING OF MISSED SAMPLES (continued)

Sample Location Collection Reason Type Code Date TLD Q-209-1 07/01/05- TLD was not changed out at the end of the 10/01/05 3rd quarter.

TLD Q-209-1 07/01/05- TLD reading reflected 3rd and 4th quarter 10/01/05 combined reading.

SW Q-33 01/07/05 No sample; water frozen.

SW Q-34 01/07/05 No sample; water frozen.

SW Q-33 01/14/05 No sample; water frozen.

SW Q-34 01/14/05 No sample; water frozen.

SW Q-33 01/21/05 No sample; water frozen.

SW Q-34 01/21/05 No sample; water frozen.

SW Q-33 01/28/05 No sample; water frozen.

SW Q-34 01/28/05 No sample; water frozen.

SW Q-33 02/04/05 No sample; water frozen.

SW Q-34 02/04/05 No sample; water frozen.

SW Q-33 02/18/05 No sample; water frozen.

TLD Quad Cities 02/26/05 TLDs Q-07-1, 2 found missing during weekly check. A different company removed fence TLDs were mounted on.

Collector placed spares Q2058084 (Q-07-1) and Q2058086 (Q-07-2).

A Q-01 10/14/05 No sample; power out; unable to field check pump.

A/I Q-01 10/21/05 No sample; power out.

SW Q-33 12/09/05 No sample; water frozen.

SW Q-34 12/09/05 No sample; water frozen.

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Table D-2 LISTING OF MISSED SAMPLES (continued)

Sample Location Collection Reason Type Code Date SW Q-33 12/16/05 No sample; water frozen.

SW Q-34 12/16/05 No sample; water frozen.

SW Q-33 12/23/05 No sample; water frozen.

SW Q-34 12/23/05 No sample; water frozen.

The overall sample recovery rate indicates that the appropriate procedures and equipment are in place to assure reliable program implementation.

E. Program Changes Beginning the third quarter 2005, Teledyne Brown Engineering Environmental Services became the primary laboratory and Environmental Inc. (Midwest Labs) became the QC laboratory. Due to the change, the data tables and summary table presented in this report will appear different from previously submitted reports. This year, only the detected and non-detected results will be presented in the data tables. As a result of this change, the first half of the year data tables will display LLD (Lower Limit of Detection) values for non-detected nuclides and the second half of the year data tables will display MDC (Minimum Detectable Concentration) values for non-detected nuclides. The summary table will include a longer list of gamma nuclides. The data points for non-detects in the figures will consist of LLD values for the first half of the year and MDC values for the second half of the year.

Airborne particulate samples were collected weekly at nine locations (Q-01, Q-02, Q-03, Q-04, Q-07, Q-13, Q-16, Q-37 and Q-38). Five locations were analyzed weekly (Q-01, Q-02, Q-03, Q-04 and Q-07) for the first half of the year, per the Quad Cities ODCM. All nine locations were analyzed weekly the second half of the year.

The air iodine samples were replaced biweekly and sent to the lab for analysis. Five locations were analyzed biweekly (Q-01, Q-02, Q-03, Q-04 and Q-07) for the first half of the year, per the Quad Cities ODCM. All nine locations were analyzed biweekly the second half of the year.

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IV. Results and Discussion A. Aquatic Environment

1. Surface Water Samples were taken weekly and composited monthly at two locations (Q-33 and Q-34). Of these locations only Q-33 located downstream, could be affected by Quad Cities' effluent releases.

The following analyses were performed.

Gross Beta Samples from all locations were analyzed for concentrations of gross beta (Table C-1.1, Appendix C). The values ranged from 2.9 to 6.5 pCi/I. Concentrations detected were consistent with those detected in previous years and the control location (Figure C-1, Appendix C). The required LLD was met.

Tritirm Quarterly composites of weekly collections were analyzed for tritium activity (Table C-1.2, Appendix C). The values ranged from

<166 to 223 pCi/l. Concentrations detected were consistent with those detected in previous years and the control location (Figure C-2, Appendix C). The 2000 pCi/L OCDM and contractually required 200 pCi/L LLDs were met.

Gamma Spectrometry Samples from both locations were analyzed for gamma emitting nuclides (Table C-1.3, Appendix C). No nuclides were detected and all required LLDs were met.

2. Ground Water Quarterly grab samples were collected at two locations (Q-35 and Q-36). Both locations could be affected by Quad Cities' effluent releases. The following analyses were performed:

Tritiim Quarterly grab samples from the locations were analyzed for tritium activity (Table C-11.1, Appendix C). The values ranged from <175 to <200 pCi/A (Figure C-3, Appendix C). The 2000 pCi/L OCDM and contractually required 200 pCi/L LLDs were met.

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Gamma Snpectrometrv Samples from all locations were analyzed for gamma emitting nuclides (Table C-11.2, Appendix C). No nuclides were detected and all required LLDs were met.

3. Fish Fish samples comprised of various commercially and recreationally important species were collected at two locations (Q-24 and Q-29) semiannually. Location Q-24 could be affected by Quad Cities' effluent releases. The following analysis was performed:

Gamma Spectrometry The edible portion of fish samples from both locations was analyzed for gamma emitting nuclides (Table C-111.1, Appendix C).

No nuclides were detected and all required LLDs were met.

4. Sediment Aquatic sediment samples were collected at one location (Q-39) semiannually. The location, located downstream, could be affected by Quad Cities' effluent releases. The following analysis was performed:

Gamma Spectrometry Sediment samples from Q-39 were analyzed for gamma emitting nuclides (Table C-IV.1, Appendix C). Cesium-137 was found in one sample at a concentration of 90 pCi/kg dry. The activity detected was consistent with those detected in the pre-operational years. No other Quad Cities fission or activation products were detected and all required LLDs were met.

B. Atmospheric Environment

1. Airborne

a. Air Particulates Continuous air particulate samples were collected from nine locations on a weekly basis. The nine locations were separated into three groups: Near site samplers within 4 km of the site (Q-01, Q-02, Q-03 and Q-04), far field samplers 16 of 206

between 4 and 10 km from the site (Q-13, Q-16, Q-37, Q-38) and the Control sampler between 10 and 30 km from the site (Q-07). Far field samples are not required to be analyzed unless the respective near field sample results are inconsistent with previous measurements and radioactivity is confirmed as having its origin in airborne effluents from the station, or at the discretion of the Onsite Dose Calculation Manual (ODCM) coordinator. Starting with the third quarter 2005, all far field samples were analyzed. The following analyses were performed:

GMsSS Beta Weekly samples were analyzed for concentrations of beta emitters (Table C-V.1 and C-V.2, Appendix C).

Detectable gross beta activity was observed at all locations.

Comparison of results among the four groups aid in determining the effects, if any, resulting from the operation of QCNPS. The results from the near site locations (Group I) ranged from <7 to 55 E-3 pCi/M 3 with a mean of 23 E-3 pCi/m 3 . The results from the far field locations (Group l1l) ranged from <6 to 56 E-3 pCi/M 3 with a mean of 24 E-3 pCi/n 3 . The results from the Control location (Group IV) ranged from 8 to 57 E-3 pCi/m 3 with a mean of 25 E-3 pCi/m 3 . Comparison of the 2005 air particulate data with previous years data indicate no effects from the operation of QCNPS. In addition a comparison of the weekly mean values for 2005 indicate no notable differences among the three groups (Figures C-4 through C-6, Appendix C).

Gamma Sppetromptry Weekly samples were composited quarterly and analyzed for gamma emitting nuclides (Table C-V.3, Appendix C). No nuclides were detected and all required LLDs were met.

b. Airborne Iodine Continuous air samples were collected from nine locations (Q-01, Q-02, Q-03, Q-04, Q-07, Q-13, Q-16, Q-37, and Q-38) and analyzed biweekly for 1-131 (Table C-VI.1, Appendix C). Far field samples are not required to be analyzed unless the respective near field (onsite and near site) sample results are inconsistent with previous 17 of 206

measurements and radioactivity is confirmed as having its origin in airborne effluents from the station, or at the discretion of the ODCM coordinator. All results were less than the MDC and the required LLD was met.

2. Terrestrial

a. Milk Samples were collected from one location (Q-26) biweekly May through October and monthly November through April.

The following analyses were performed:

lodline 31 Milk samples from the location were analyzed for concentrations of 1-131 (Table C-VI1.1, Appendix C). All results were less than the MDC and the required LLD was met.

Gamma Spectrometry Each milk sample was analyzed for concentrations of gamma emitting nuclides (Table C-VII.2, Appendix C). No nuclides were detected and all required LLDs were met.

b. Food Products Food product samples were collected at four locations plus a control location (Q-Quad 1 - Control, Q-Quad 1, Q-Quad 2, Q-Quad 3, and Q-Quad 4) annually during growing season.

Four locations, (Q-Quad 1, Q-Quad 2, Q-Quad 3 and Q-Quad 4) could be affected by Quad Cities' effluent releases. The following analysis was performed:

Gamma Spectrometry Samples from all locations were analyzed for gamma emitting nuclides (Table C-VIII.1, Appendix C). No nuclides were detected and all required LLDs were met.

C. Ambient Gamma Radiation Ambient gamma radiation levels were measured utilizing Harshaw thermoluminescent dosimeters. Forty TLD locations were established 18 of 206

around the site. Results of TLD measurements are listed in Tables C-IX.1 to C-IX.3, Appendix C.

Most TLD measurements were below 30 mR/quarter, with a range of 16 to 31 mR/quarter. A comparison of the Inner Ring, Outer Ring and Other data to the Control Location data, indicate that the ambient gamma radiation levels from all the locations were comparable.

The TLDs at the control location Q-07 were found missing on 02/26/2005, see Table D-2 Listing of Missed Samples, page 9. The TLDs were missing for less than or equal to one week and had negligible impact on the monitoring at the control location.

D. Independent Spent Fuel Storage Installation QCNPS commenced use of an Independent Spent Fuel Storage Installation (ISFSI) in Dec 2005. There were no measurable changes in ambient gamma and radiation level as a result of ISFSI operations.

E. Land Use Survey A Land Use Survey conducted during August 2005 around QCNPS was performed by Environmental Inc. (Midwest Labs) for Exelon Nuclear to comply with the Quad Cities' Offsite Dose Calculation Manual. The purpose of the survey was to document the nearest resident and milk producing animals in each of the sixteen 22 1/2degree sectors around the site. There were no changes required to the QCNPS REMP, as a result of this survey. The results of this survey are summarized below.

19 of 206

Distance in Miles from QCNPS Sector Residence Livestock Milk Farm Miles Miles Miles AN 0.6 2.7 B NNE 3.8 5.4 CNE 1.3 D ENE 2.9 2.9 EE 2.3 2.7 F ESE 2.8 3.1 3.1 G SE 2.5 5.5 H SSE 1.1 3.6 6.6 JS 0.8 1.6 K SSW 3.2 L SW 2.9 3.3 M WSW 2.2 2.2 NW 2.6 4.3 4.6 P WNW 2.7 3.8 Q NW 2.6 2.6 R NNW 2.1 2.2 F. Errata Data There were several minor typographical errors in the 2004 Annual Radiological Environmental Operating Report. A review of 2001-2003 AREORs indicated similar typographical errors. These errors are described below. The corrected pages from each report are contained in Appendix E of this report.

2004 The reported fish Cs-1 34 and Cs-1 37 LLDs were incorrect in Table 5.0-4.

The reported airborne 1-131 LLD was incorrect in Table 5.0-5.

2003 The reported airborne 1-131 LLD was incorrect in Table 5.0-5.

2002 The reported airborne 1-131 LLD was incorrect in Table 5.0-5.

2001 The reported airborne 1-131 LLD was incorrect in Table 5.0-5.

The reported airborne 1-131 LLD was incorrect in Table 5.0-6.

The reported surface water "other ODCM required gamma' LLDs were incorrect in Table 5.0-6.

20 of 206

G. Summary of Results - Inter-Laboratory Comparison Program The primary and secondary laboratories analyzed Performance Evaluation (PE) samples of air particulate, air iodine, milk, soil, vegetation and water matrices (Appendix D). The PE samples, supplied by Analytics Inc.,

Environmental Resource Associates (ERA) and DOE's Mixed Analyte Performance Evaluation Program (MAPEP), were evaluated against the following pre-set acceptance criteria:

1. Analytics Evaluation Criteria Analytics' evaluation report provides a ratio of laboratory results and Analytics' known value. Since flag values are not assigned by Analytics, TBE-ES evaluates the reported ratios based on internal QC requirements, which are based on the DOE MAPEP criteria.

2. ERA Evaluation Criteria ERA's evaluation report provides an acceptance range for control and warning limits with associated flag values. ERA's acceptance limits are established per the USEPA, NELAC, state specific PT program requirements or ERA's SOP for the Generation of Performance Acceptance Limits, as applicable. The acceptance limits are either determined by a regression equation specific to each analyte or a fixed percentage limit promulgated under the appropriate regulatory document.

3. DOE Evaluation Criteria MAPEP's evaluation report provides an acceptance range with associated flag values.

The MAPEP defines three levels of performance: Acceptable (flag =

"A"), Acceptable with Warning (flag = 'W"), and Not Acceptable (flag = uN"). Performance is considered acceptable when a mean result for the specified analyte is +/- 20% of the reference value.

Performance is acceptable with warning when a mean result falls in the range from +/-20% to +/-30% of the reference value (i.e., 20% <

bias < 30%). If the bias is greater than 30%, the results are deemed not acceptable.

For the primary laboratory, 18 out of 19 analytes met the specified acceptance criteria. One sample did not meet the specified acceptance criteria for the following reason:

21 of 206

1. Teledyne Brown Engineering's Analytics' September 2005 air particulate Fe-59 ratio of 1.35 exceeded the upper control limit of 1.30 due to a new technician not counting the air particulate in a petri dish.

For the secondary laboratory, 19 out of 23 analytes met the specified acceptance criteria. Four samples did not meet the specified acceptance criteria for the following reasons:

1. Environmental Inc.'s ERA's November 2005 water Gross Alpha result of 41.1 pCi/L exceeded the upper control limit of 33.4 pCi/L.

This was due to using an Am-241 efficiency instead of a Th-232 efficiency when counting the sample. Using the correct efficiency gave a result of 27.0 pCi/L, which fell within the control limits.

2. Environmental Inc.'s ERA's November 2005 water Ra-228 result of 5.5 pCi/L exceeded the upper control limit of 5.0 pCi/L due to presence of radium daughters. Delay in counting 100 minutes gave a result of 4.01 pci/L, which fell within the control limits.

3. Environmental Inc.'s MAPEP's January 2005 air particulate Sr-90 result of 2.2 Bq/kg exceeded the upper control limit of 1.76 Bq/kg.

Reanalysis result was 1.56 Bq/kg, which fell within the control limits.

4. Environmental Inc.'s MAPEP's July 2005 soil Am-241 result of 48.4 exceeded the lower control limit of 56.77 Bq/kg due to incorrect sample weight being used in the calculation. When recalculated with the correct sample weight, the result was 97.0 Bq/kg, which fell within the control limits.

The Inter-Laboratory Comparison Program provides evidence of "in control" counting systems and methods, and that the laboratories are producing accurate and reliable data.

22 of 206

APPENDIX A RADIOLOGICAL ENVIRONMENTAL MONITORING REPORT

SUMMARY

23 of 206

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 1ST QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 1ST QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN

_ LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS SURFACE WATER GR-B 4 4 6.5 5.9 6.5 Q-33 INDICATOR 0 (PCI/LITER) (1/2) (1/2) (1/2) CORDOVA 3.1 MILES SSW OF SITE H-3 2 200 <LLD <LLD 0 GAMMA 4 MN-54 15 <LLD <LLD 0 CO-58 15 <LLD <LLD 0 FE-59 30 <LLD <LLD 0 CO-60 15 <LLD <LLD 0 ZN-65 30 <LLD <LLD NB-95 15 <LLD <LLD 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 1ST QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 1ST QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS ZR-95 30 <LLD <LLD 0 1-131 15 <LLD <LLD 0 CS-134 15 <LLD <LLD 0 CS-137 18 <LLD <LLD 0 BA-140 60 <LLD <LLD 0 LA-140 15 <LLD <LLD 0 GROUND WATER H-3 2 200 <LLD N/A 0 (PCI/LITER)

GAMMA 2 MN-54 15 <LLD N/A 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-i RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, IST QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: IST QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS CO-58 15 <LLD N/A 0 FE-59 30 <LLD N/A 0 CO-60 15 <LLD N/A 0 ZN-65 30 <LLD N/A 0 NB-95 15 <LLD N/A 0 ZR-95 30 <LLD N/A 0 CS-134 15 <LLD N/A 0 CS-137 18 <LLD N/A 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 1ST QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: IST QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS BA-140 60 <LLD N/A LA- 140 15 <LLD N/A 0 AIR PARTICULATE GR-B 65 10 27 29 29 Q-07 CONTROL 0 (E-3 PCI/CU.METER) (52/52) (13/13) (13/13) CLINTON (12/49) (17/52) (17/52) 8.9 MILES NE OF SITE GAMMA 5 MN-54 N/A <LLD <LLD 0 CO-58 N/A <LLD <LLD 0 FE-59 N/A <LLD <LLD 0 CO-60 N/A <LLD <LLD 0 ZN-65 N/A <LLD <LLD 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-i RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 1ST QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 1ST QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS ZRNB-95 N/A <LLD <LLD 0 CS-134 10 <LLD <LLD CS-137 10 <LLD <LLD 0 BALA 140 N/A <LLD <LLD 0

> AIR IODINE 1-131 30 70 <LLD <LLD 0 ti (E-3 PCI/CU.METER)

MILK 1-131 3 I <LLD N/A 0 (PCI/LITER)

GAMMA 3 MN-54 N/A <LLD N/A 0 CO-58 N/A <LLD N/A 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 1ST QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 1ST QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN. STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS FE-59 N/A <LLD N/A 0 CO-60 N/A <LLD N/A 0 ZN-65 N/A <LLD N/A 0 ZRNB-95 N/A <LLD N/A 0 CS-134 15 <LLD N/A 0 CS-137 18 <LLD N/A 0 BA-140 60 <LLD N/A 0 LA-140 15 <LLD N/A 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 1ST QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 1ST QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS DIRECT RADIATION TLD-QUARTERLY 78 N/A 25.2 N/A 31.0 Q-203-2* INDICATOR 0 (MILLI-ROENTGEN/QTR) (78/78) (1/1)

(22/31) 5.0 MILES NE OF SITE

Locations Q-203-2 and Q-211-1 had identical results of 31.0 mR. Only Q-203-2 is detailed in this summary.

CA) 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

Oh t.J 0i C.

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 2ND QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 2ND QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS SURFACE WATER GR-B 6 4 5.5 5.2 5.5 Q-33 INDICATOR 0 (PCI/LITER) (1/3) (1/3) (1/3) CORDOVA 3.1 MILES SSW OF SITE H-3 2 200 <LLD <LLD 0 GAMMA 6 MN-54 15 <LLD <LLD 0 CO-58 15 <LLD <LLD 0 00 FE-59 30 <LLD <LLD 0 CO-60 15 <LLD <LLD 0 ZN-65 30 <LLD <LLD NB-95 15 <LLD <LLD 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 2ND QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 2ND QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS ZR-95 30 <LLD <LLD 0 1-13 1 15 <LLD <LLD 0 CS-134 15 <LLD <LLD 0 CS-137 18 <LLD <LLD 0 BA-140 60 <LLD <LLD 0 LA-140 15 <LLD <LLD GROUND WATER H-3 2 200 <LLD N/A 0 (PCI/LITER)

GAMMA MN-54 15 <LLD N/A 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F) a.h 0

tSi C) an%

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 2ND QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 2ND QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS CO-58 15 <LLD N/A 0 FE-59 30 <LLD N/A 0 CO-60 15 <LLD N/A 0 ZN-65 30 <LLD N/A 0 NB-95 15 <LLD N/A 0 l

ZR-95 30 <LLD N/A 0 CS-134 15 <LLD N/A 0 CS-137 18 <LLD N/A 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-i RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 2ND QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 2ND QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS BA-140 60 <LLD N/A 0 LA-140 15 <LLD N/A 0 FISH GAMMA 4 (PCI/KG WET) MN-54 130 <LLD <LLD 0 CO-58 130 <LLD <LLD 0 FE-59 260 <LLD <LLD 0 CO-60 130 <LLD <LLD 0 ZN-65 260 <LLD <LLD ZRNB-95 N/A <LLD <LLD 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 2ND QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 2ND QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) . (LLD) MEASUREMENTS CS-134 130 <LLD <LLD 0 CS-137 150 <LLD <LLD 0 BALA140 N/A <LLD <LLD 0 SEDIMENT GAMMA I (PCI/KG) MN-54 N/A <LLD N/A 0 t-'

CO-58 N/A <LLD N/A 0 FE-59 N/A <LLD N/A 0 CO-60 N/A <LLD N/A 0 ZN-65 N/A <LLD N/A LA Ln MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M) 0 FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F) to all

TABLE A-i RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 2ND QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 2ND QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) - (LLD) MEASUREMENTS ZRNB-95 N/A <LLD N/A 0 CS-134 150 <LLD N/A 0 CS-137 180 <LLD N/A 0 BALA140 N/A <LLD N/A 0 I: 10 19 22 22 Q-07 CONTROL 0 AIR PARTICULATE GR-B 65 (E-3 PCI/CU.METER) (52/52) (12/13) (12/13) CLINTON (11/28) (16/36) (16/36) 8.9 MILES NE OF SITE GAMMA 5 MN-54 N/A <LLD <LLD 0 CO-58 N/A <LLD <LLD 0 FE-59 N/A <LLD <LLD 0 W

L.J MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M) 0 FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

I-h 0bi

._ .

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 2ND QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 2ND QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS CO-60 N/A <LLD <LLD 0 ZN-65 N/A <LLD <LLD 0 ZRNB-95 N/A <LLD <LLD 0 CS-134 10 <LLD <LLD 0 CS-137 10 <LLD <LLD 0 BALA140 N/A <LLD <LLD 0 AIR IODINE 1-131 35 70 <LLD <LLD (E-3 PCI/CU.METER)

MILK 1-131 5 <LLD N/A 0 (PCtILITER)

MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 2ND QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 2ND QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS GAMMA 5 MN-54 N/A <LLD N/A 0 CO-58 N/A <LLD N/A 0 FE-59 N/A <LLD N/A 0 CO-60 N/A <LLD N/A 0 ZN-65 N/A <LLD N/A 0 ZRNB-95 N/A <LLD N/A 0 CS-134 15 <LLD N/A 0 CS-137 18 <LLD N/A 0 w

0, MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M) 0 FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

Iti 0o CD 0

TABLE A-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 2ND QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 2ND QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS BA-140 60 <LLD N/A 0 LA- 140 15 <LLD N/A 0 DIRECT RADIATION TLD-QUARTERLY 80 N/A 17.7 17.0 22.0 Q-214-2* INDICATOR 0 (MILLI-ROENTGEN/QTR) (78/78) (2/2) (1/1)

(16/22) (17/17) 4.4 MILES WNW OF SITE I

aE

Locations Q-214-2 and Q-215-2 had identical results of 22.0 mR. Only Q-214-2 is detailed in this summary.

MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 3RD QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 3RD QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS SURFACE WATER GR-B 6 4 4.4 4.7 4.7 Q-34 CONTROL 0 (PCI/LITER) (3/3) (3/3) (3/3) CAMANCHE - UPSTREAM (2.9/5.8) (4.2/5.3) (4.2/5.3) 4.4 MILES NNE OF SITE H-3 2 200 223 211 223 Q-33 INDICATOR 0 (1/1) (1/1) (1/1) CORDOVA 3.1 MILES SSW OF SITE GAMMA 6 MN-54 15 <LLD <LLD 0 CO-58 15 <LLD <LLD 0 FE-59 30 <LLD <LLD 0 CO-60 15 <LLD <LLD ZN-65 30 <LLD <LLD NB-95 15 <LLD <LLD 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 3RD QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 3RD QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS ZR-95 30 <LLD <LLD 0 1-131 15 <LLD <LLD 0 CS-134 15 <LLD <LLD 0 CS-137 18 <LLD <LLD 0 00 BA-140 60 <LLD <LLD 0 LA-140 15 <LLD <LLD 0 GROUND WATER H-3 2 200 <LLD N/A (PCI/LITER)

GAMMA 2 MN-54 15 <LLD N/A 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 3RD QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 3RD QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS CO-58 15 <LLD N/A 0 FE-59 30 <LLD N/A 0 CO-60 15 <LLD N/A 0 ZN-65 30 <LLD N/A 0 NB-95 15 <LLD N/A 0 ZR-95 30 <LLD N/A 0 CS-134 15 <LLD N/A 0 CS-137 18 <LLD N/A 0 db.3 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M) 0 FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

Ih an

TABLE A-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 3RD QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 3RD QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS BA-140 60 <LLD N/A 0 LA-140 15 <LLD N/A 0 AIR PARTICULATE GR-B 116 10 22 22 24 Q-13 INDICATOR 0 (E-3 PCI/CU.METER) (101/103) (13/13) (13/13) PRINCETON (7/48) (11/41) (10/48) 4.7 MILES SW OF SITE GAMMA 9 MN-54 N/A <LLD <LLD 0 0~

k)

CO-58 N/A <LLD <LLD 0 FE-59 N/A <LLD <LLD 0 CO-60 N/A <LLD <LLD 0 ZN-65 N/A <LLD <LLD 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-i RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 3RD QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 3RD QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS ZRNB-95 N/A <LLD <LLD 0 CS-134 10 <LLD <LLD CS-137 10 <LLD <LLD 0 BALA140 N/A <LLD <LLD 0

> AIR IODINE 1-131 63 70 <LLD <LLD 0 S! (E-3 PCI/CU.METER)

MILK 1-131 7 <LLD N/A 0 (PCI/LITER)

GAMMA 7 MN-54 N/A <LLD N/A 0 CO-58 N/A <LLD N/A 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M) o FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F) th 05

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 3RD QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 3RD QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS FE-59 N/A <LLD N/A 0 CO-60 N/A <LLD N/A 0 ZN-65 N/A <LLD N/A 0 ZRNB-95 N/A <LLD N/A 0 CS-134 15 <LLD N/A CS-137 18 <LLD N/A 0 BA-140 60 <LLD N/A 0 LA-140 15 <LLD N/A 0 a,

MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F) 0 bi

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 3RD QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 3RD QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS FOOD PRODUCTS GAMMA 10 (PCI/KG WET) MN-54 N/A <LLD <LLD 0 CO-58 N/A <LLD <LLD 0 FE-59 N/A <LLD <LLD 0 CO-60 N/A <LLD <LLD 0 ZN-65 N/A <LLD <LLD 0 ZRNB-95 N/A <LLD <LLD 0 1-131 60 <LLD <LLD 0 CS-134 60 <LLD <LLD 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 3RD QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 3RD QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS CS-137 80 <LLD <LLD 0 BALA140 N/A <LLD <LLD 0 DIRECT RADIATION TLD-QUARTERLY 79 N/A 19.6 18.0 26.0 Q-211-2 INDICATOR 0 (MILLI-ROENTGEN/QTR) (77/77) (2/2) (1/1)

(16/26) (18/18) 4.5 MILES SW OF SITE t'j MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-i RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 4TH QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 4TH QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS SURFACE WATER GR-B 6 4 5.3 5.7 5.7 Q-34 CONTROL 0 (PCI/LITER) (3/3) (3/3) (3/3) CAMANCHE - UPSTREAM (4.7/5.8) (5.1/6) (5.1/6) 4.4 MILES NNE OF SITE H-3 2 200 <LLD <LLD 0 GAMMA MN-54 15 <LLD <LLD 0 CO-58 15 <LLD <LLD 0

>t I'.)

FE-59 30 <LLD <LLD CO-60 15 <LLD <LLD 0 ZN-65 30 <LLD <LLD 0 NB-95 15 <LLD <LLD 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 4TH QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 4TH QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS ZR-95 30 <LLD <LLD 0 1-131 15 <LLD <LLD 0 CS-134 15 <LLD <LLD 0 CS-137 18 <LLD <LLD 0 1~j BA-140 60 <LLD <LLD 0 LA-140 15 <LLD <LLD 0 GROUND WATER H-3 200 <LLD N/A 0 (PCI/LITER)

GAMMA 2 MN-54 15 <LLD N/A 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 4TH QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 4TH QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS CO-58 15 <LLD N/A 0 FE-59 30 <LLD N/A 0 CO-60 15 <LLD N/A 0 ZN-65 30 <LLD N/A 0 I\) NB-95 15 <LLD N/A 0 ZR-95 30 <LLD N/A 0 CS-134 15 <LLD N/A 0 CS-137 18 <LLD N/A MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M) 0 FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F) ai a%1

TABLE A-i RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 4TH QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 4TH QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS BA-140 60 <LLD N/A 0 LA-140 15 <LLD N/A 0 FISH GAMMA 4 (PCI/KG WET) MN-54 130 <LLD <LLD 0 CO-58 130 <LLD <LLD 0 FE-59 260 <LLD <LLD 0 CO-60 130 <LLD <LLD 0 ZN-65 260 <LLD <LLD 0 ZRNB-95 N/A <LLD <LLD 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 4TH QUARTER 2005 NAME OF FACILITY: . QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 4TH QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS CS-134 130 <LLD <LLD 0 CS-137 150 <LLD <LLD 0 BALA140 N/A <LLD <LLD 0 SEDIMENT GAMMA I (PCI/KG DRY) MN-54 N/A <LLD N/A 0 I',

io CO-58 N/A <LLD N/A 0 FE-59 N/A <LLD N/A 0 CO-60 N/A <LLD N/A 0 ZN-65 N/A <LLD N/A 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 4TH QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 4TH QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS ZRNB-95 N/A <LLD N/A 0 CS-134 150 <LLD N/A 0 CS-137 180 90 N/A 90 Q-39 INDICATOR 0 (1/l) (1/1) CORDOVA - DOWNSTREAM MISSISSIPPI RIVER 0.8 MILES SSW OF SITE BALA140 N/A <LLD N/A 0 0

tw co AIR PARTICULATE GR-B 115 10 24 25 26 Q-13 INDICATOR 0 (E-3 PCIICU.METER) (102/102) (13/13) (13/13) PRINCETON (10/56) (11/57) (13/56) 4.7 MILES SW OF SITE GAMMA 9 MN-54 N/A <LLD <LLD 0 CO-58 N/A <LLD <LLD 0 FE-59 N/A <LLD <LLD 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M) 0 FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F) t-h Isj 0) a.'

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 4TH QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 4TH QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS CO-60 N/A <LLD 0 ZN-65 N/A <LLD <LLD 0 ZRNB-95 N/A <LLD <LLD 0 CS-134 10 <LLD <LLD 0 CS-137 10 <LLD <LLD 0 BALA140 N/A <LLD <LLD 0 53 70 <LLD <LLD 0 AIR IODINE 1-131 (E-3 PCI/CU.METER) 4 I <LLD N/A 0 MILK 1-131 (PCI/LITER)

MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

To FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F) toh N)

C)0A

TABLE A-l RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 4TH QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 4TH QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS GAMMA 4 MN-54 N/A <LLD N/A 0 CO-58 N/A <LLD N/A 0 FE-59 N/A <LLD N/A 0 CO-60 N/A <LLD N/A 0 ZN-65 N/A <LLD N/A 0 ZRNB-95 N/A <LLD N/A CS-134 15 <LLD N/A 0 CS-137 18 <LLD N/A 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-i RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 4TH QUARTER 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 4TH QUARTER, 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS BA-140 60 <LLD N/A 0 LA-140 15 <LLD N/A 0 DIRECT RADIATION TLD-QUARTERLY 80 N/A 24.8 24.5 43.0 Q-209-1 INDICATOR 0 (MILLI-ROENTGEN/QTR) (78/78) (2/2) (1/1)

(21/43*) (24/25) 4.7 MILES S OF SITE On ^ TLD WAS IN SERVICE JULY THROUGH DECEMBER MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M) 0 FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F) oh 05 Tol

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS SURFACE WATER GR-B 22 4 5.1 5.3 5.3 Q-34 CONTROL 0 (PCI/LITER) (8/11) (8/11) (8/11) CAMANCHE - UPSTREAM (2.9/6.5) (4.2/6) (4.2/6) 4.4 MILES NNE OF SITE H-3 8 200 223 211 223 Q-33 INDICATOR 0 (1/4) (1/4) (1/4) CORDOVA 3.1 MILES SSW OF SITE GAMMA 22 MN-54 15 <LLD <LLD 0 CO-58 15 <LLD <LLD 0 FE-59 30 <LLD <LLD CO-60 15 <LLD <LLD 0 ZN-65 30 <LLD <LLD 0 NB-95 15 <LLD <LLD 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS ZR-95 30 <LLD <LLD 0 1-131 15 <LLD <LLD 0 CS-134 15 <LLD <LLD 0 CS-137 18 <LLD <LLD 0 BA-140 60 <LLD <LLD LA-140 15 <LLD <LLD 0 GROUND WATER H-3 8 200 <LLD N/A 0 (PCI/LITER)

GAMMA 8 MN-54 15 <LLD N/A 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-i RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS CO-58 15 <LLD N/A 0 FE-59 30 <LLD N/A 0 CO-60 15 <LLD N/A 0 ZN-65 30 <LLD N/A 0 NB-95 15 <LLD N/A 0 ZR-95 30 <LLD N/A 0 CS- 134 15 <LLD N/A 0 CS-137 18 <LLD N/A Ln MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M) 0 FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F) 0-h 0

a,

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS BA-140 60 <LLD N/A 0 LA- 140 15 <LLD N/A 0 FISH GAMMA 8 (PCI/KG WET) MN-54 130 <LLD <LLD 0 CO-58 130 <LLD <LLD 0 FE-59 260 <LLD <LLD 0 CO-60 130 <LLD <LLD 0 ZN-65 260 <LLD <LLD 0 ZRNB-95 N/A <LLD <LLD 0 0o MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F) 0 Ha.

Tol

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS CS-134 130 <LLD <LLD 0 CS-137 150 <LLD <LLD 0 BALA140 N/A <LLD <LLD 0 SEDIMENT GAMMA 2 (PCI/KG DRY) MN-54 N/A <LLD N/A 0 00 CO-58 N/A <LLD N/A 0 FE-59 N/A <LLD N/A 0 CO-60 N/A <LLD N/A 0 ZN-65 N/A <LLD N/A 0 as MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F) 0tioh)

CY)

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS ZRNB-95 N/A <LLD N/A 0 CS-134 150 <LLD N/A 0 CS-137 180 90 N/A 90 Q-39 INDICATOR 0 (1/2) (1/2) CORDOVA - DOWNSTREAM MISSISSIPPI RIVER 0.8 MILES SSW OF SITE BALA 140 N/A <LLD N/A 0 AIR PARTICULATE GR-B 361 10 23 24 25 Q-1 3 INDICATOR 0 (E-3 PCI/CU.METER) (307/309) (51/52) (26/26) PRINCETON (7/56) (11/57) (10/56) 4.7 MILES SW OF SITE GAMMA 28 MN-54 N/A <LLD <LLD 0 CO-58 N/A <LLD <LLD FE-59 N/A <LLD <LLD 0 01%

MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M) 0 FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F) 1-h 0-

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS CO-60 N/A <LLD <LLD 0 ZN-65 N/A <LLD <LLD 0 ZRNB-95 N/A <LLD <LLD 0 CS-134 10 <LLD <LLD 0 4 CS-137 10 <LLD <LLD 0 BALA140 N/A <LLD <LLD 0 AIR IODINE 1-131 181 70 <LLD <LLD 0 (E-3 PCI/CU.METER)

MILK 1-131 19 I <LLD N/A 0 (PCI/LITER)

MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS GAMMA 19 MN-54 N/A <LLD N/A 0 CO-58 N/A <LLD N/A 0 FE-59 N/A <LLD N/A 0 CO-60 N/A <LLD N/A 0 ZN-65 N/A <LLD N/A 0 ZRNB-95 N/A <LLD N/A 0 CS-134 15 <LLD N/A 0 CS-137 18 <LLD N/A 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS BA-140 60 <LLD N/A LA-140 15 <LLD N/A 0 FOOD PRODUCT GAMMA 10 (PCI/KG WET) MN-54 N/A <LLD <LLD CO-58 N/A <LLD <LLD 0 FE-59 N/A <LLD <LLD 0 CO-60 N/A <LLD <LLD 0 ZN-65 N/A <LLD <LLD 0 ZRNB-95 N/A <LLD <LLD 0 MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FOR QUAD CITIES NUCLEAR POWER STATION, 2005 NAME OF FACILITY: QUAD CITIES DOCKET NUMBER: 50-254 &50-265 LOCATION OF FACILITY: CORDOVA, IL REPORTING PERIOD: 2005 INDICATOR CONTROL LOCATION WITH HIGHEST ANNUAL MEAN LOCATIONS LOCATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN MEAN MEAN STATIONS # NUMBER OF PATHWAY SAMPLED ANALYSES ANALYSES LOWER LIMIT (F) (F) (F) NAME NONROUTIME (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT) (LLD) MEASUREMENTS 1-131 60 <LLD <LLD 0

CS-134 60 <LLD <LLD 0 CS-137 80 <LLD <LLD 0 BALA140 N/A <LLD <LLD 0 DIRECT RADIATION TLD-QUARTERLY 317 N/A 24.8 19.8 430 Q-209-1 INDICATOR (MILLI-ROENTGEN/QTR) (311/31 1) (6/6) (3/4)

(16/43*) (17/25) (18/43*) 4.7 MILES S OF SITE

TLD 209-1 was in service July through December and read 43 mrem which equals an average of 21.5 mrem/quarter.

MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)

FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

APPENDIX B LOCATION DESIGNATION, DISTANCE & DIRECTION, AND SAMPLE COLLECTION & ANALYTICAL METHODS 67 of 206

TABLE B-1: Radiological Environmental Monitoring Program - Sampling Locations, Distance and Direction, Quad Cities Nuclear Power Station, 2005 Location Location Description Distance & Direction From Site A Siurface Wate Q-33 Cordova (indicator) 3.1 miles SSW 0-34 Camanche, Upstream (control) 4.4 miles NNE B Gmrund/WpIl Water Q-35 McMillan Well (indicator) 1.5 miles S Q-36 Cordova Well (indicator) 3.3 miles SSW r Milk - hi-wepklv / monthlv Q-26 Bill Stanley Dairy (indicator) 3.5 miles ESE D Air Partriflatpa / Air lodinp Q-01 Onsite 1 (indicator) 0.5 miles N Q-02 Onsite 2 (indicator) 0.4 miles ENE Q-03 Onsite 3 (indicator) 0.6 miles S Q-04 Nitrin (indicator) 1.7 miles NE Q-07 Clinton (control) 8.9 miles NE Q-13 Princeton (indicator) 4.7 miles SW Q-16 Low Moor (indicator) 5.7 miles NNW Q-37 Meredosia Road (indicator) 4.4 miles ENE Q-38 Fuller Road (indicator) 4.7 miles E F Fish Q-24 Pool #14 of Mississippi River, Downstream (indicator) 0.5 miles SW Q-29 Mississippi River, Upstream (control) 1.0 miles N F. Sedinment Q-39 Cordova, Downstream on Mississippi River (indicator) 0.8 miles SSW fi Frd Prmdi uitrt Quadrant 1 Janet Price 6.0 miles NE Quadrant 2 Dale Nimmic 3.0 miles ESE Quadrant 3 Amy Johnston 1.8 miles S Quadrant 4 Mike Fawcett 4.5 miles NW Control Charles Leavens 9.5 miles NE

, gAA __,_. T n I-i .- n~mnpnr, I;ogmeIry - I I I~nnLerRun 0-101-1 0.6 miles N Q-101-2 0.9 miles N Q-102-1 1.3 miles NNE 0-102-3 1.4 miles NNE Q-103-1 and -2 1.2 miles NE Q-104-1 1.1 miles ENE 0-104-2 0.9 miles ENE Q-105-1 and -2 0.8 miles E Q-106-2 and -3 0.7 miles ESE 0-107-2 0.7 miles SE Q-107-3 0.8 miles SE 0-108-1 1.0 miles SSE Q-108-2 0.9 miles SSE B-1 68 of 206

TABLE B-1: Radiological Environmental Monitoring Program - Sampling Locations, Distance and Direction, Quad Cities Nuclear Power Station, 2005 Location Location Description Distance & Direction From Site Q-109-1 0.9 miles S Q-109-2 1.2 miles S 0-111-1 2.6 miles SW Q-111-2 2.5 miles SW Q-112-1 2.5 miles WSW 0-112-2 2.2 miles WSW Q-113-1 and-2 2.5 miles W Q-114-1 2.1 miles WNW Q-114-2 2.5 miles WNW Q-115-1 2.6 miles NW 0-115-2 2.3 miles NW Q-116-1 2.3 miles NNW Q-116-3 2.4 miles NNW Ou iar Ring Q-201-1 and -2 4.2 miles N Q-202-1 4.4 miles NNE 0-202-2 4.8 miles NNE Q-203-1 4.7 miles NE Q-203-2 5.0 miles NE 0-204-1 4.7 miles ENE Q-204-2 4.5 miles ENE Q-205-1 4.7 miles E Q-205-4 4.8 miles E Q-206-1 and -2 4.8 miles ESE Q-207-1 and -4 4.7 miles SE Q-208-1 4.3 miles SSE Q-208-2 4.9 miles SSE Q-209-1 and -4 4.7 miles S Q-210-1 and -4 4.1 miles SSW Q-211-1 and-2 4.5 miles SW 0-212-1 5.4 miles WSW Q-212-2 4.4 miles WSW Q-213-1 4.3 miles W Q-213-2 4.8 miles W Q-214-1 4.7 miles WNW Q-214-2 4.4 miles WNW Q-215-1 5.0 miles NW Q-215-2 4.2 miles NW Q-216-1 4.6 miles NNW Q-216-2 4.3 miles NNW Q-01 Onsite I (indicator) 0.5 miles N Q-02 Onsite 2 (indicator) 0.4 miles ENE Q-03 Onsite 3 (indicator) 0.6 miles S Q-04 Nitrin (indicator) 1.7 miles NE Q-13 Princeton (indicator) 4.7 miles SW Q-16 Low Moor (indicator) 5.7 miles NNW Q-37 Meredosia Road (indicator) 4.4 miles ENE Q-38 Fuller Road (indicator) 4.7 miles E rDntmfO Q-07 8.9 miles NE B-2 69 of 206

TABLE B-2: Radiological Environmental Monitoring Program - Summary of Sample Collection and Analytical Methods, Quad Cities Nuclear Power Station, 2005 Sample Analysis Sampling Method Analytical Procedure Number Medium Surface Water Gamma Spectroscopy Monthly composite from TBE, TBE-2007 Gamma emitting radioisotope analysis weekly grab samples.

Env. Inc., GS-01 Determination of gamma emitters by

_amma spectroscoDy Surface Water Gross Beta Monthly composite from TBE, TBE-2008 Gross Alpha and/or gross beta activity in weekly grab samples. various matrices Env. Inc., W(DS)-01 Determination of gross alpha and/or

_ross beta in water (dissolved solids or total residue)

Surface Water Tritium Quarterly composite TBE, TBE-2011 Tritium analysis in drinking water by liquid from weekly grab scintillation samples.

Env. Inc., T-02 Determination of tritium inwater (direct method)

Ground Water Gamma Spectroscopy Quarterly grab samples. TBE, TBE-2007 Gamma emitting radioisotope analysis Env. Inc., GS-01 Deterriination of gamma emitters by gamma soectroscoDv Ground Water Tritium Quarterly grab samples. TBE, TBE-201 1 Tritium analysis in drinking water by liquid scintillation Env. Inc., T-02 Determination of tritium in water (direct method)

Fish Gamma Spectroscopy Semi-annual samples TBE-2007 Gamma emitting radioisotope analysis collected via electroshocking or other Env. Inc., GS-01 Determination of gamma emitters by techniquesamma sDectnrscoov Sediment Gamma Spectroscopy Semi-annual grab TBE, TBE-2007 Gamma emitting radioisotope analysis samples Env. Inc., GS-01 Determination of gamma emitters by

_amma spectroscoDv Air Particulates Gross Beta One-week composite of TBE, TBE-2008 Gross Alpha and/or gross beta activity in continuous air sampling various matrices through glass fiber filter paper Env. Inc., AP-02 Determination of gross alpha and/or gross beta in air particulate filters Air Particulates Gamma Spectroscopy Quarterly composite of TBE, TBE-2007 Gamma emitting radioisotope analysis each station Env. Inc., GS-O01 Determination of gamma emitters by gamma spectroscopv Air Iodine Gamma Spectroscopy Biweekly composite of TBE, TBE-2007 Gamma emitting radioisotope analysis continuous air sampling through charcoal filter Env. Inc., 1-131-02 Determination of 1-131 incharcoal canisters by aamma soectroscoov (batch method)

B-3 70 of 206

TABLE B-2: Radiological Environmental Monitoring Program - Summary of Sample Collection and Analytical Methods, Quad Cities Nuclear Power Station, 2005 Sample Analysis Sampling Method Analytical Procedure Number Medium Milk 1-131 Bi-weekly grab sample TBE, TBE-2012 Radioiodine in various matrices when cows are on pasture. Monthly all Env. Inc., 1-131-01 Determination of 1-131 in milk by anion other times exchange Milk Gamma Spectroscopy Bi-weekly grab sample TBE, TBE-2007 Gamma emitting radioisotope analysis when cows are on pasture. Monthly all Env. Inc., GS-01 Determination of gamma emitters by other times gamma spectroscoDv Food Products Gamma Spectroscopy Annual grab samples. TBE, TBE-2007 Gamma emitting radioisotope analysis Env. Inc., GS-01 Determination of gamma emitters by aamma soectroscoov TLD Thermoluminescence Quarterly TLDs Global Dosimetry Dosimetry II B-4 71 of 206

+

^ Aft 2441 a, 2644 a

EL 1t141 0 am OF 204&

11 2004

7a S 2*7-4 m -1 a 21043

uXmp0Jlngss Aitr Samplimn Sites

a ouM sa" LO Q4M Ouh*ls I Q7MC11"60(c)

Q2OW~riNef QX13hioc"-

qb3 OwlIe No.3 Qb1 LoW Of Q" M4tM Q47 mobfa RId Q-n wooer Row Figure B-1 Quad Cities Outer Ring TLDs and Air Sampling Sites, 2005 B-5 72 of 206

Figure B-2 Quad Cities Inner Ring TLD Locations, 2005 B-6 73 of 206

M11116 FisA. Water sand Sediment Snm le Lcations 444 IPm014 4oMhppi UV,Mv 444 Ca k (C)

Q4-2am Staa DriS Mc6etin W w isppi Rhr.Uptwn Q-36 Qa ba WOl Q4 Co*w 4 C1*v F39 r*tftm uS W o~r Figure B-3 Quad Cities Milk, Fish, Water and Sediment Sampling Locations, 2005 B-7 74 of 206

K APPENDIX C DATA TABLES AND FIGURES PRIMARY LABORATORY 75 of 206

TABLE C-1.1 CONCENTRATIONS OF GROSS BETA IN SURFACE WATER SAMPLES COLLECTED IN THE VICINITY OF QUAD CITIES NUCLEAR POWER STATION, 2005 RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMA COLLECTION PERIOD Q-33 Q-34 JAN (1) (1)

FEB < 4.0 (1) 5.9 +/- 1.2 (1)

MAR 6.5 +/- 1.3 < 4.0 APR 5.5 +/- 1.1 5.2 +/- 1.2 MAY < 4.0 < 4.0 JUN < 4.0 < 4.0 JUL 2.9 +/- 1.8 4.7 +/- 2.0 AUG 4.6 +/- 1.8 5.3 +/- 1.9 SEP 5.8 +/- 1.9 4.2 +/- 1.8 OCT 4.7 +/- 1.7 6.0 +/- 1.8 NOV 5.2 +/- 1.8 5.9 +/- 1.8 DEC 5.8 +/- 2.0 5.1 +/-1.9 TABLE C4.2 CONCENTRATIONS OF TRITIUM IN SURFACE WATER SAMPLES COLLECTED IN THE VICINITY OF QUAD CITIES NUCLEAR POWER STATION, 2005 RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMA COLLECTION PERIOD Q-33 Q-34 JAN-MAR < 200 < 200 APR-JUN < 200 < 200 JUL-SEP 22:3 +/- 112 211 +/- 113 OCT-DEC < 166 < 168 DUE TO VENDOR CHANGE, < VALUES ARE LLD VALUES JANUARY THROUGH JUNE AND MDC VALUES JULY THROUGH DECEMBER (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-1 76 of 206

TABLE C-1.3 CONCENTRATIONS OF GAMMA EMITTERS IN SURFACE WATER SAMPLES COLLECTED IN THE VICINITY OF QUAD CITIES NUCLEAR POWER STATION, 2005 RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMA STC COLLECTION MN-54 CO-58 FE-59 CO-60 ZN-65 NB-95 ZR-95 1-131 CS-134 CS-137 BA-140 LA-140 PERIOD Q-33 JAN (1)

FEB < 15 < 15 < 30 < 15 < 30 < 15 < 30 < 15 < 15 < 18 <60 <15 MAR < 15 < 15 < 30 < 15 < 30 < 15 < 30 < 15 < 15 < 18 <60 <15 APR < 15 < 15 < 30 < 15 < 30 < 15 < 30 < 15 < 15 < 18 <60 <15 MAY < 15 < 15 < 30 < 15 < 30 < 15 < 30 < 15 < 15 < 18 <60 < 15 JUN < 15 < 15 < 30 < 15 < 30 < 15 < 30 < 15 < 15 < 18 <60 < 15 JUL <1 <1 <3 < 1 < 2 <1 < 2 <3 < 1 < 1 <39 <12 AUG < 2 <2 < 5 < 2 < 4 < 2 < 4 < 14 <2 <2 < 21 <7 SEP <6 <5 < 14 <5 < 10 < 7 < 9 < 14 <6 <7 <31 <12 OCT <5 < 4 <9 <4 < 8 < 6 < 9 < 14 <4 <5 <32 <9 NOV <4 <4 < 11 < 5 < 8 < 5 < 8 < 12 <4 <5 <28 < 12 DEC < 2 <2 <6 <4 < 5 < 3 < 5 <7 <2 <3 < 16 <5 0

Q-34 JAN (1)

FEB < 15 < 15 < 30 < 15 < 30 < 15 < 30 < 15 < 15 < 18 <60 <15 MAR < 15 < 15 < 30 < 15 < 30 < 15 < 30 < 15 < 15 < 18 <60 <15 APR < 15 < 15 < 30 < 15 < 30 < 15 < 30 < 15 < 15 < 18 < 60 <15 MAY < 15 < 15 < 30 < 15 < 30 < 15 < 30 < 15 < 15 <18 <60 < 15 JUN < 15 < 15 < 30 < 15 < 30 < 15 < 30 < 15 < 15 < 18 <60 < 15 JUL <1 <1 < 3 < 1 < 2 < 1 < 2 <3 < 1 < 1 <42 <14 AUG < 1 <2 <4 <1 < 3 < 2 < 3 < 11 < 1 <1 < 17 <5 SEP <4 <5 <6 <4 < 10 < 4 <9 < 10 <4 <5 < 25 <9 OCT <3 <4 <8 <4 < 7 < 4 <8 < 12 <3 <3 <26 <9 NOV <5 <5 < 11 <4 <9 < 6 <9 < 13 <5 <5 < 33 < 10 DEC <3 <4 <8 < 3 < 7 < 4 <7 < 10 <3 <3 < 23 <8 DUE TO VENDOR CHANGE, <VALUES ARE LLD VALUES JANUARY THROUGH JUNE AND MDC VALUES JULY 4 THROUGH DECEMBER (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION

TABLE C-11.1 CONCENTRATIONS OF TRITIUM IN GROUND WATER SAMPLES COLLECTED IN THE VICINITY OF QUAD CITIES NUCLEAR POWER STATION, 2005 RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMA COLLECTION PERIOD 0-35 0-36 JAN-MAR < 200 < 200 APR-JUN < 200 < 200 JUL-SEP < 175 < 176 OCT-DEC ' 186 < 187 DUE TO VENDOR CHANGE, < VALUES ARE LLD VALUES JANUARY THROUGH JUNE AND MDC VALUES JULY THROUGH DECEMBER C-3 78 of 206

TABLE C-11.2 CONCENTRATIONS OF GAMMA EMITTERS IN GROUND WATER SAMPLES COLLECTED IN THE VICINITY OF QUAD CITIES NUCLEAR POWER STATION, 2005 RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMA STC COLLECTION PERIOD MN-54 CO-58 FE-59 CO-60 ZN-65 NB-95 ZR-95 CS-134 CS-1 37 BA-140 LA-140 m -

Q-35 JAN < 15 < 15 < 30 < 15 < 30 < 15 < 30 < 15 < 18 <60 < 15 APR < 15 < 15 < 30 < 15 < 30 < 15 < 30 < 15 < 18 < 60 < 15 JUL <6 < 7 < 11 < 6 < 11 <6 < 11 < 5 <7 <35 < 10 OCT <4 < 3 < 11 < 3 < 6 < 5 < 8 < 4 <4 <27 <9 Q-36 JAN < 15 < 15 < 30 < 15 < 30 < 15 < 30 < 15 < 18 < 60 < 15 APR < 15 < 15 < 30 < 15 < 30 < 15 < 30 < 15 < 18 < 60 < 15 JUL < 7 < 9 < 20 < 7 < 18 <9 < 16 <6 <8 < 43 < 8 OCT < 6 < 5 < 13 <6 < 10 < 6 < 11 <6 <6 < 31 < 10 C)

DUE TO VENDOR CHANGE, < VALUES ARE LLD VALUES JANUARY THROUGH JUNE AND MDC VALUES JULY THROUGH DECEMBER

TABLE C-111.1 CONCENTRATIONS OF GAMMA EMITTERS IN FISH SAMPLES COLLECTED IN THE VICINITY OF QUAD CITIES NUCLEAR POWER STATION, 2005 RESULTS IN UNITS OF PCI/KG WET +/- 2 SIGMA COLLECTION MN-54 CO-58 FE-59 CO-60 ZN-65 ZRNB-95 CS-134 CS-137 BALA-140 STC PERIOD Q-24 Golden Redhorse 05/18/05 < 130 < 130 < 260 < 130 < 260 < 200 < 100 < 100 < 300 Channel Catfish 05/18/05 < 130 < 130 < 260 < 130 < 260 < 200 < 100 < 100 < 300 Largemouth Bass 10/11/05 < 84 < 91 < 196 < 57 < 170 < 94 < 75 < 82 < 115 Channel Catfish 10/11/05 < 54 < 53 < 132 < 57 < 106 < 49 < 61 < 58 < 161 Q-29 Walleye 05/18/05 < 130 < 130 < 260 < 130 < 260 < 200 < 100 < 100 < 300 River Carpsucker 05/18/05 < 130 < 130 < 260 < 130 < 260 < 200 < 100 < 100 < 300 Common Carp 10/11/05 < 62 < 38 < 131 < 48 < 100 < 48 < 44 < 55 < 91 Channel Catfish 10/11/05 < 52 < 67 < 128 < 67 < 140 < 70 < 58 < 57 < 150 en 00 DUE TO VENDOR CHANGE, < VALUES ARE LLD VALUES JANUARY THROUGH JUNE AND MDC VALUES JULY THROUGH DECEMBER 0

Oh 0)

TABLE C4V.1 CONCENTRATIONS OF GAMMA EMITTERS IN SEDIMENT SAMPLES COLLECTED INTHE VICINITY OF QUAD CITIES NUCLEAR POWER STATION, 2005 RESULTS IN UNITS OF PCI/KG DRY i 2 SIGMA STC COLLECTION MN-54 CO-58 FE-59 CO-60 ZN-65 ZRNB-95 CS-134 CS-137 BALA-140 PERIOD

_A_AA PA _ _

< 150

~~~~-< 100_A_--A A

AAA AA_._AsA 600 < 100 < 600 < 200 < 150 < 180 < 600 Q-39 05120105 <

10/06/05 < 77 < 76 < 165 < 84 < 176 < 91 < 68 90 t 53 < 172 a)

DUE TO VENDOR CHANGE, < VALUES ARE LLD VALUES JANUARY THROUGH JUNE AND MDC VALUES JULY THROUGH DECEMBER

TABLE C-V.1 CONCENTRATIONS OF GROSS BETA IN AIR PARTICULATE SAMPLES COLLECTED IN THE VICINITY OF QUAD CITIES NUCLEAR POWER STATION, 2005 RESULTS IN UNITS OF E-3 PCI/CU METER +/- SIGMA GROUP I I GROUP 11 l GROUP III

.

Q-38 Q-07 A

Q-13 Q-16 Q-37 A AX WEEK U-04 A . _

Q-01 Q-02 Q-U3 I w -

1 32 +/- 4 35 +/- 4 43 +/- 5 40 5 (1) (1) (1) (1) 38+/-5 2 47

4 39 +/- 4 47 +/- 4 49+/- 4 52 +/- 4 3 37 +/- 4 39 +/- 4 48 +/- 5 40. 4 43 +/- 5 4 22+/- 4 20 +/- 4 25 +/- 4 27 4 29 +/- 4 5 28 i 4 27 +/- 4 28 +/- 4 26+/- 4 28 +/- 4 6 26 +/- 4 24 +/- 3 24 +/- 3 22+/- 3 23 +/- 3 7 26 +/- 4 25 +/- 4 26 +/- 4 28 +/- 4 28 +/- 4 8 31 +/- 3 29 +/- 3 32 +/- 3 33 +/- 3 33 +/- 3 9 24 +/- 5 17 +/- 4 22 +/- 4 16+/- 4 17 +/- 4 10 21 +/- 4 25 +/- 4 21 +/- 4 22. 4 24 +/- 5 11 18 t 3 20 +/- 3 18 +/- 3 20 +/-,3 19 +/- 3 12 12 +/- 3 13 +/- 3 14 +/- 3 16 +/-A3 17 +/- 3 13 22 +/- 3 22 +/- 3 25 +/- 3 24 3 28 +/- 4 14 19 +/- 3 18 +/- 3 21 +/- 4 20+/- 4 20 +/- 3 15 19 +/- 4 25 +/- 4 22 +/- 4 23 +/-A4 21 +/- 4 16 23 +/- 3 24 +/- 3 28 +/- 4 22 +/-A3 28 +/- 3 17 15 +/- 3 15 +/- 3 17 +/- 3 17+/- 3 18 +/- 3 18 25 +/- 4 23 +/- 4 24 +/- 4 25 +/- 4 27 +/- 4 19 19 +/- 4 19 +/- 4 19 +/- 4 18 +/- 4 22 +/- 4 20 14 +/- 3 13 +/- 3 15 +/- 3 18 +/- 3 17 +/- 3 21 18 +/- 4 16 +/- 3 17 +/- 3 15 +/- 3 16 +/- 3 22 17 +/- 3 17 +/- 3 18 +/- 4 17 3 17 +/- 4 23 18 +/- 3 18 +/- 3 19 +/- 3 15 3 < 10 24 13 +/- 4 12 +/- 4 14 +/- 4 11 +/-4 18 +/- 3 25 23 +/- 3 22 +/- 3 24 +/- 3 24+/- 3 24 +/- 3 26 26 i 3 19 +/- 3 28 +/-A3 26 +/-A3 36 +/- 4 27 7 7 5 11+/- 5 11 5 10 +/-4 11 +/-4 11 +/-5 8+/-5 11+/-4 28 25 +/- 5 19 +/-5 25 5 19 5 27 +/- 5 24 +/- 5 24 +/-5 19+/-5 25 5 29 19 +/- 5 14 +/- 5 22 5 12 5 18 +/- 5 16 +/- 5 18 +/-5 21+/-5 18+/-5 30 13 +/- 5 14 +/- 5 14+/- 4 15+/- 5 12 +/- 4 11 +/-4 11 +/-4 13 5 12+/-4 31 23 +/- 5 30 +/- 6 28+/- 5 25+/- 5 28 +/- 6 25 +/- 5 28 +/-5 28 5 30+/-6 32 26 +/- 5 21 +/- 5 25+/- 5 23+/- 5 23 +/- 5 25 +/- 5 21 +/-5 26+/-5 22+/-5 33 22 +/- 5 16 +/- 5 20 5 15 ,5 21 +/- 5 18 +/-5 22 +/- 5 16+/-5 16 5 34 9 +/- 4 (2) 13 +/-5 11 +/-5 16 +/- 5 11 +/-4 11 +/-5 6 12+/-5 35 22 +/- 4 30 +/- 6 22. 4 27. 5 29 +/- 5 24 +/-5 22 +/-4 28+/-5 21+/-4 36 29 +/- 5 26 : 5 27 5 31+/- 5 32 +/- 5 31 +/-5 24 +/- 5 37+/-5 34+5 37 36 +/- 5 29 +/- 5 41 5 24 4 48A+/-6 41 +/-5 41 +/- 5 44A+/-6 41+/-5 38 31 +/- 5 31 +/- 5 31+/- 5 30+/- 5 35 +/- 5 30 +/- 5 30 i 5 34A+/-5 28+/-5 39 14 +/- 4 18 +/- 4 19 4 15 +/-4 19 +/-4 14 +/-,4 14 +/-4 16 +/-4 17 +/-,4 40 26 +/- 6 15 +/-t4 14 +/- 4 12 +/-4 13 +/- 4 14 +/-4 14 +/-4 16 +/- 4 15 +/- 4 41 (2) 13 +/-4 11 i4 t17 4 19 +/- 5 21 i 5 17 +/-4 18 +/-4 19+/-.4 42 (2) 16 +/- 4 19 4 16 4 18 +/-4 19 +/-,4 19 i 4 22A+/-4 18 +/- 4 43 17 +/- 7 16 +/-4 11 +/-3 15+/-4 17 +/- 4 17 +/-A4 17 +/-4 13 +/-,3 18+/-4 44 27 +/- 5 24 +/- 5 33 +/- 5 32 5 28 +/- 5 26 +/- 5 30 i 5 25 +/-5 25+/-5 45 28 +/- 5 27 +/- 5 31 +/- 5 36+/- 5 36 +/- 5 33 +/-5 32 +/-5 24A+/-5 37A+/-5 46 12 +/- 4 17 +/- 4 14 +/- 4 14 +/-4 14 +/-4 16 +/-4 14 i 4 10 +/-4 17 +/-4 47 17 +/- 4 15 +/-4 12 I 4 14 +/- 4 16 t 4 13 +/-4 13 +/-4 15 +/-4 11 4 48 15 +/- 4 17 +/- 4 16 +/-4 18 +/- 4 22 +/- 4 18 +/-A4 15 44 16+/-4 17+/-4 49 32 +/- 5 30 +/- 5 30 +/- 5 34 +/-5 40 +/- 6 36 +/-5 32 +/-5 29 +/-5 30+/-5 50 27 +/- 5 26 +/- 5 25 +/- 5 23 +/- 5 29 +/- 5 29 +/-5 25 +/-5 23A+/-5 25+/-5 51 50 +/- 6 50+/- 6 46 +/- 6 55 +/- 6 56 +/- 6 53 +/-6 55 +/-6 55A+/-6 57+/-6 52 33 +/- 5 30 +/- 5 33+/-5 34A.5 36A+/-5 38 +/- 5 38 +/- 5 30^+/-5 32 5 MEAN 23 +/- 17 22 +/- 16 24 +/- 18 23 +/- 19 25 +/- 23 24 +/- 21 23 +/- 21 23 +/- 22 24 +/- 20 (1) SEE PROGRAM CHANGES SECTION FOR EXPLANATION (2) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION

' THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING BOTH THE MDA AND POSITIVE VALUES C-7 82 of 206

TABLE C-V.2 MONTHLY AND YEARLY MEAN VALUES OF GROSS BETA CONCENTRATIONS (E-3 PCI/CU METER) INAIR PARTICULATE SAMPLES COLLECTED IN THE VICINITY OF QUAD CITIES NUCLEAR POWER STATION, 2005 GROUP I - NEAR SITE LOCATIONS GROUP II - FAR FIELD LOCATIONS GROUP III - CONTFIOL LOCATIONS COLLECTION MIN. MAX. MEAN +/- COLLECTION MIN. MAX. MEAN +/- COLLECTION MIN. MAX. MEAN +/-

PERIOD 2 SD PERIOD 2 SD PERIOD 2 SD I .

12131/04 - 01/28/05 20 49 37 +/- 19 12/31/04 - 01/28/05 (1) (1) (1) 12/31/04 - 01/28/05 29 52 41 +/- 19 O0/28/05 - 02/26/05 22 33 27 +/- 6 01/28/05 - 02/26/05 01/28/05 - 02/26/05 23 33 28 +/- 8 03/,04/05 - 04/02/05 12 25 20 +/- 8 03/04/05 - 04/02/05 03/04/05 - 04/02/05 17 28 22 +/- 10 04/.08/05 - 04/29/05 15 28 21 +/- 8 04/08/05 - 04/29/05 04/08/05 - 04/29/05 18 28 22 +/- 10 04/.29/05 - 06/03/05 13 25 18 +/- 7 04/29/05 - 06/03/05 04/29/05 - 06/03/05 16 27 20 +/- 9 06,i04/05 - 07/02/05 11 28 20 11 06/04/05 - 07/02/05 06/04/05 - 07/02/05 8 36 22 +/- 23 07/'02/05 - 07/29/05 < 7 25 16 11 07/02/05 - 07/29/05 8 27 16 +/- 12 07/02/05 - 07/29/05 11 25 17 +/- 13 071'29/05 - 09/02/05 9 30 21 +/- 12 07/29/05 - 09/02/05 6 29 21+/- 13 07/29/05 - 09/02/05 12 30 20 +/- 13 O9Rf02/05 - 09/30/05 14 41 27 +/- 15 09/02/05 - 09/30/05 14 48 31+/- 21 09/02/05 - 09/30/05 17 41 30 +/- 21 09/'30/05 - 11/03/05 11 26 15 i 8 09/30/05 - 11/03/05 13 28 18 +/- 8 09/30/05 - 11/03/05 15 25 19 +/- 7 11/ '03/05 - 12/02/05 12 36 19 +/- 15 11/03/05 - 12/02/05 10 36 19+/- 16 11/03/05 - 12/02/05 11 37 20 +/- 23 12/'02/05 - 12/30/05 23 55 35 +/- 19 12/02/05 - 12/30/05 23 56 38+/- 22 12/02/05 - 12/30/05 25 57 36 +/- 28 C) co 01/28/05 - 12/28/05 < 7 55 23 +/- 14 01/28/05 - 12/28/05 < 6 56 24 +/- 17 01/28/05 - 12/28/05 8 57 25 +/- 15 (1) SEE PROGRAM CHANGES SECTION FOR EXPLANATION 0T O-h 0

To Cs

TABLE C-V.3 CONCENTRATIONS OF GAMMA EMITTERS IN AIR PARTICULATE SAMPLES COLLECTED IN THE VICINITY OF QUAD CITIES NUCLEAR POWER STATION, 2005 RESULTS IN UNITS OF E-3 PCI/CU METER +/- 2 SIGMA STC COLLECTION MN-54 C0-58 FE-59 C0-60 ZN-65 ZRNB-95 CS-134 CS-137 BALA140 PERIODl Q-01 12/31/04 04/02/05 < 10.0 < 10.0 < 15.0 < 10.0 < 40.0 < 10.0 < 10.0 < 1u.u < MM.

04/02/05 07/02/05 < 10.0 < 10.0 < 15.0 < 10.0 < 40.0 < 10.0 < 10.0 < 10.0 < 25.0 07/02/05 09/30/05 <4.2 < 3.9 < 18 < 1.9 < 13 < 6.4 < 4.7 < 4.1 < 87 09/30/05 12/30/05 < 2.8 < 2.2 < 4.9 < 6.4 < 8.4 < 2.8 < 2.4 < 3.0 < 9.3 Q-02 12/31/04 04/02/05 < 10.0 < 10.0 < 15.0 < 10.0 < 40.0 < 10.0 < 10.0 < 10.0 < 25.0 04/02105 07/02/05 < 10.0 < 10.0 < 15.0 < 10.0 < 40.0 < 10.0 < 10.0 < 10.0 < 25.0 07/02/05 09/30/05 < 2.8 < 3.1 < 5.0 < 3.6 < 4.9 < 4.3 < 2.2 < 1.7 < 79 09/30/05 12/30/05 < 3.0 < 2.2 < 6.9 < 2.4 < 5.4 < 2.8 < 2.6 < 2.5 < 13 C-)

D Q-03 12131/04 04/02/05 < 10.0 < 10.0 < 15.0 < 10.0 < 40.0 < 10.0 < 10.0 < 10.0 < 25.0 04/02105 07/02/05 < 10.0 < 10.0 < 15.0 < 10.0 < 40.0 < 10.0 < 10.0 < 10.0 < 25.0 07/02/05 09/30/05 < 2.1 < 2.4 < 8.8 < 1.8 < 5.4 < 2.7 < 2.0 < 1.7 < 40 09/30/05 12130/05 < 2.3 < 2.7 < 3.7 < 2.5 < 5.6 < 2.9 < 2.3 < 1.9 < 10 Q-04 12/31/04 04/02105 < 10.0 < 10.0 < 15.0 < 10.0 < 40.0 < 10.0 < 10.0 < 10.0 < 25.0 04/02/05 07/02/05 < 10.0 < 10.0 < 15.0 < 10.0 < 40.0 < 10.0 < 10.0 < 10.0 < 25.0 07/02/05 09/30/05 < 2.7 < 2.1 < 7.1 < 1.5 < 6.0 < 4.5 < 1.3 < 2.0 < 69 09/30/05 12/30/05 < 2.8 < 2.8 < 6.0 < 1.0 < 7.3 < 2.5 < 2.5 < 2.2 < 12 Q-07 12/31/04 04/02/05 < 10.0 < 10.0 < 15.0 < 10.0 < 40.0 < 10.0 < 10.0 < 10.0 < 25.0 04/02/05 07/02/05 < 10.0 < 10.0 < 15.0 < 10.0 < 40.0 < 10.0 < 10.0 < 10.0 < 25.0 07/02/05 09/30/05 < 3.2 < 3.5 < 8.6 < 2.9 < 6.7 < 5.2 < 2.8 < 3.2 < 31 09/30/05 12/30/05 < 2.8 < 2.9 < 6.4 < 2.4 < 5.9 < 2.4 < 3.1 < 2.7 < 16 DUE TO VENDOR CHANGE, <VALUES ARE LLD VALUES JANUARY THROUGH JUNE AND MDC VALUES JULY THROUGH DECEMBER 0

A-h a.'

TABLE C-V.3 CONCENTRATIONS OF GAMMA EMITTERS IN AIR PARTICULATE SAMPLES COLLECTED IN THE VICINITY OF QUAD CITIES NUCLEAR POWER STATION, 2005 RESULTS IN UNITS OF E-3 PCI/CU METER +/- 2 SIGMA STC COLLECTION MN-54 CO-58 FE-59 CO-60 ZN-65 ZRNB-95 CS-134 CS-137 BALA140 PERIOD I

Q-13 (1)

(1) 07/02/05 09/30/05 <4.3 < 6.1 < 19 < 4.1 < 9.5 < 6.7 < 4.4 < 4.2 < 91 09/30/05 12/30/05 < 2.7 <3.2 < 6.8 < 3.0 < 8.8 < 3.1 < 3.4 < 3.3 < 7.6 Q-16 (1)

(1) 07/02/05 09/30/05 < 3.3 < 4.7 < 14 < 3.3 < 11 < 5.4 < 4.9 < 3.9 < 45 09/30/05 12/30/05 < 2.8 < 3.0 < 7.7 < 2.5 < 5.6 < 3.1 < 3.1 < 2.8 < 15 0-37 (1)

C)

(1) 07/02/05 09/30/05 < 2.4 < 4.2 < 2.9 < 3.0 < 7.4 < 2.8 < 1.7 < 2.4 < 69 09/30/05 12/30/05 < 2.4 < 2.1 < 3.3 < 2.9 < 3.6 < 2.5 < 1.9 < 2.3 < 12 Q-38 (1)

(1) 07/02/05 09/30/05 < 1.9 < 3.8 < 11 < 3.6 < 6.8 < 5.1 < 2.1 < 1.5 < 17 09/30/05 12/30/05 < 2.3 < 2.7 < 6.6 < 3.0 < 4.8 < 2.7 < 2.2 < 2.2 < 12 DUE TO VENDOR CHANGE, < VALUES ARE LLD VALUES JANUARY THROUGH JUNE AND MDC VALUES JULY THROUGH DECEMBER (1) SEE PROGRAM CHANGES SECTION FOR EXPLANATION

TABLE C-VI.1 CONCENTRATIONS OF 1-131 INAIR IODINE SAMPLES COLLECTED IN THE VICINITY OF QUAD CITIES NUCLEAR POWER STATION, 2005 RESULTS IN UNITS OF E-3 PCI/CU METER + SIGMA GROUPI l GROUP II l GROUP III WEEK Q-01 0-02 Q-03 Q-04 Q-13 0-16 Q-37 Q-38 0-07 2 <70 <70 <70 <70 (1) (1) (1) (1) <70 3

4 <70 <70 <70 <70 <70 5

6 <70 <70 <70 <70 <70 7

8 <70 <70 <70 <70 <70 9

10 <70 <70 <70 <70 <70 11 12 <70 <70 <70 <70 <70 13 14 <70 <70 <70 <70 <70 15 16 <70 <70 <70 <70 <70 17 18 <70 <70 <70 <70 <70 19 20 < 70 < 70 < 70 < 70 < 70 21 22 < 70 < 70 < 70 < 70 < 70 23 24 < 70 < 70 < 70 < 70 < 70 25 26 < 70 < 70 < 70 < 70 < 70 27 28 <8 <15 <14 <16 <16 <14 <14 <15 <14 29 30 < 18 < 18 <17 < 17 < 16 < 15 < 15 < 10 < 15 31 32 < 12 < 12 < 12 < 12 < 15 < 15 < 15 < 15 <8 33 34 < 14 < 14 < 13 < 14 < 16 < 10 < 16 < 16 < 13 35 36 <24 <27 <23 <24 <12 <16 <16 <16 <15 37 38 <16 <16 <15 <16 <17 <16 <17 <11 <8 39 40 < 21 < 19 < 18 < 14 < 14 < 13 < 14 < 14 < 18 41 42 (2) <20 < 13 < 19 <20 < 19 < 19 '19 < 19 43 44 <9 <9 <9 <9 <17 <16 <14 <14 <10 45 1 46 <18 <18 <17 <18 <29 <28 <30 <20 <28 47 48 <10 <15 < 15 <15 <13 <13 <13 <13 <10 49 50 <13 <20 <20 <20 <17 <17 <17 <17 <20 51 52 <14 <15 <14 <14 <26 <26 <24 <24 <8 DUE TO VENDOR CHANGE, < VALUES ARE LLD VALUES JANUARY THROUGH JUNE AND MDC VALUES JULY THROUGH DECEMBER (1) SEE PROGRAM CHANGES SECTION FOR EXPLANATION (2) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-11 86 of 206

TABLE C-VII.1 CONCENTRATIONS OF 1-131 IN MILK SAMPLES COLLECTED IN THE VICINITY OF QUAD CITIES NUCLEAR POWER STATION, 2005 RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMA COLLECTION INDICATOR FARM PERIOD Q-26 01/07/05 < 1.0 02/04/05 < 1.0 03/04/05 < 1.0 04/02/05 < 1.0 05/06/05 < 1.0 05/20/05 < 1.0 06/03/05 < 1.0 06/17/05 < 1.0 07/02/05 < 1.0 07115/05 < 0.6 07/29/05 < 0.9 08/12/05 < 0.4 08/26/05 < 0.3 09/09/05 < 0.7 09/23/05 < 0.5 10/07/05 < 0.7 10/21/05 < 0.9 11/04/05 < 0.6 12/02/05 < 0.7 DUE TO VENDOR CHANGE, < VALUES ARE LLD VALUES JANUARY THROUGH JUNE AND MDC VALUES JULY THROUGH DECEMBER C-12 87 of 206

TABLE C-VII.2 CONCENTRATIONS OF GAMMA EMITTERS IN MILK SAMPLES COLLECTED IN THE VICINITY OF QUAD CITIES NUCLEAR POWER STATION, 2005 RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMA STC COLLECTION MN-54 CO-58 FE-59 CO-60 ZN-65 ZRNB-95 CS-134 CS-137 BA-140 LA-140 PERIOD Q-26 01/07/05 ' 10 < 10 < 15 < 10 ' 15 < 10 < 15 < 18 < 60 < 15 02/04/05 < 10 < 10 < 15 < 10 < 15 < 10 < 15 < 18 < 60 < 15 03/04/05 < 10 < 10 < 15 < 10 < 15 < 10 < 15 < 18 < 60 < 15 04/02/05 ' 10 < 10 < 15 < 10 < 15 < 10 < 15 < 18 < 60 < 15 05/06/05 < 10 ' 10 < 15 < 10 < 15 < 10 < 15 < 18 < 60 < 15 05/20/05 < 10 < 10 < 15 < 10 < 15 ' 10 < 15 < 18 < 60 < 15 06/03/05 < 10 < 10 < 15 < 10 < 15 < 10 < 15 < 18 < 60 < 15 06/17/05 < 10 < 10 < 15 < 10 ' 15 < 10 ' 15 < 18 < 60 < 15 07/02/05 ' 10 < 10 < 15 < 10 < 15 < 10 < 15 < 18 < 60 < 15 07/15/05 <7 <9 < 17 < 16 < 18 < 7 <6 < 8 < 39 < 14 07/29/05 < 6 <5 < 17 <6 < 17 <7 < 7 < 5 < 38 <9 08/12/05 < 4 <4 < 11 <4 < 14 < 5 < 4 < 5 < 21 <6 C) 08/26/05 <5 <6 < 12 <4 < 7 < 6 <4 < 5 < 27 <9 09109/05 <6 < 7 < 14 <8 < 15 < 7 < 6 < 6 < 38 < 12 09/23/05 <7 <7 < 18 <7 < 16 < 8 < 7 < 8 < 41 < 12 10/07/05 <6 <4 < 12 < 7 < 10 < 6 < 4 < 5 < 24 <8 10/21/05 <6 <6 < 13 <6 < 12 < 6 < 5 < 6 < 31 <9 11/04/05 < 5 <5 < 16 <6 < 14 < 6 < 5 < 7 < 32 < 11 12/02/05 <2 <2 <5 <2 <5 < 2 <2 < 2 <9 <3 DUE TO VENDOR CHANGE, <VALUES ARE LLD VALUES JANUARY THROUGH JUNE AND MDC VALUES JULY THROUGH DECEMBER

TABLE C-VIII.1 CONCENTRATIONS OF GAMMA EMITTERS IN FOOD PRODUCT SAMPLES COLLECTED IN THE VICINITY OF QUAD CITIES NUCLEAR POWER STATION, 2005 RESULTS IN UNITS OF PCI/KG WET +/- 2 SIGMA STC: COLLECTION MN-54 CO-s8 FE-59 CO-60 ZN-65 ZRNB-95 1-131 CS-1 34 CS-137 BALA140 PERIOD 0-QUAD 07120/05 < 20 < 15 < 24 <18 < 26 < 17 < 36 < 19 < 20 <32 Rhubarb Leaves 0-QUAD 1 07120105 < 14 < 13 < 31 <17 < 33 < 17 < 34 < 15 < 21 < 24 Onions MEAN 17 +/- 9 14 +/- 4 27 +/- 11 17 +/- 2 30 +/- 10 17 +/- 1 35 +/- 2 17 +/- 5 21 +/-I1 28 +/- 12

< 19 < 18 < 44 < 20 < 34 < 17 < 20 < 29 0-QUAD 2 07/20105 < 18 < 35 Rhubarb Leaves 07120105 < 21 < 23 < 52 < 24 < 43 < 19 < 28 < 31 0-QUAD 2 < 41 < 35 Onions MEAN 20 +/- 4 21 +/- 6 38 +/- 8 27 +/- 24 48 i 12 22 +/- 6 38 +/- 12 18 +/- 3 24 +/- 10 30 +/- 4 C) 0-QUAD 3 07120105 < 26 < 21 < 49 < 35 < 68 < 24 < 39 < 17 < 22 < 26 Broccoli 0-QUAD 3 07/20/05 < 15 < 15 < 31 < 16 < 32 < 16 < 32 <15 < 19 < 21 Horseradish MEAN 20 +/- 15 18 +/- 7 40 +/- 25 25 +/- 27 50 +/- 51 20 +/- 12 35 +/- 9 16 +/- 3 21 +/- 5 23

7 0-QUAD 4 07/20105 < 20 < 16 < 40 < 18 < 41 < 21 <36 <17 < 18 < 33 Cabbage 0-QUAD 4 07/20/05 <5 <5 < 12 <6 < 12 <6 <9 <5 <6 <6 Potatoes MEAN 12 +/- 20 11 +/- 16 26 +/- 39 12 +/- 18 27 i 40 13 +/- 22 22 +/- 38 11 +/- 17 12 +/- 18 20 +/- 37 0-QUAD 1 - CONTROL 07/20105 < 25 < 25 < 40 < 21 < 54 < 21 < 40 < 24 < 23 <36 Rhubarb Leaves 0-QUAD 1 - CONTROL 07/20105 < 12 < 16 < 29 <9 < 23 < 13 <24 < 11 < 11 <15 Potatoes MEAN 19+/-i18 20 +/-13 35+/- 15 15 +/-16 38+/-i44 17 +/-12 32 +/-24 17+/-i18 17 +/-17 25+/-t29 00 Lh 0

t-h

TABLE C-IX.1 QUARTERLY TLD RESULTS FOR QUAD CITIES NUCLEAR POWER STATION, 2005 RESULTS IN UNITS OF MILLI-ROENTGEN/QUARTER +/- 2 STANDARD DEVIATIONS STATION MEAN JAN-MAR APR-JUN JUL-SEP OCT-DEC CODE i2 S.D.

Q-01-1 21.3 8.7 25 17 18 25 Q-01-2 20.8 7.7 25 17 18 23 Q-02-1 22.3 8.2 26 17 21 25 Q-02-2 20.5 6.0 23 17 19 23 Q-03-1 20.8 8.1 23 16 19 25 Q-03-2 20.0 8.2 23 17 16 24 Q-04-1 21.8 7.5 23 17 21 26 Q-04-2 21.5 7.4 24 17 20 25 Q-07-1 19.7 7.6 (1) 17 18 24 Q-07-2 20.0 8.7 (1) 17 18 25 Q-13-1 21.3 7.5 24 18 18 25 Q-13-2 21.0 8.2 24 17 18 25 Q-16-1 20.0 8.5 22 16 17 25 0-16-2 20.3 7.0 22 16 19 24 Q-37-1 21.3 10 24 17 17 27 Q-37-2 19.5 +/- 5.8 22 17 17 22 Q-38-1 21.8 +/- 11 27 17 17 26 Q-38-2 20.5 +/- 5.3 23 17 20 22 Q-101-1 20.5 +/- 7.0 23 17 18 24 Q-101-2 21.5 +/- 8.4 26 17 19 24 Q-102-1 22.5 +/- 9.5 29 19 19 23 Q-102-3 21.0 +/- 9.1 27 17 18 22 Q-103-1 20.3 +/- 7.7 23 16 18 24 Q-103-2 20.5 +/- 8.4 23 16 18 25 Q-104-1 20.0 +/- 8.5 22 16 17 25 Q-104-2 20.8 +/- 7.2 23 16 20 24 Q-105-1 21.3 +/- 8.7 25 18 17 25 Q-105-2 20.8 +/- 8.9 25 16 18 24 Q-106-2 20.3 +/- 5.5 22 17 19 23 Q-106-3 19.8 +/- 6.4 23 17 17 22 Q-107-2 21.0 +/- 10 26 16 17 25 Q-107-3 21.0 +/- 8.2 25 17 18 24 Q-108-1 21.3 +/- 10 28 16 19 22 0-108-2 21.5 +/- 9.9 27 16 19 24 Q-109-1 21.8 +/- 8.2 27 17 21 22 Q-109-2 21.3 +/- 5.3 24 19 19 23 Q-111-1 22.8 +/- 6.6 26 19 21 25 Q-111-2 21.8 +/- 9.1 24 17 19 27 Q-112-1 22.0 +/- 7.3 24 18 20 26 Q-112-2 20.5 +/- 7.0 23 17 18 24 0-113-1 20.8 +/- 6.6 24 17 19 23 Q-113-2 21.3 +/- 6.8 24 17 20 24 0-114-1 20.0 +/- 6.3 22 16 19 23 Q-114-2 21.8 +/- 6.0 25 18 21 23 Q-115-1 20.5 +/- 6.8 25 17 19 21 Q-115-2 21.3 +/- 5.3 25 20 19 21 Q-116-1 22.0 +/- 8.5 27 18 19 24 Q-116-3 21.8 +/- 10 27 17 18 25 (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-15 90 of 206

TABLE C-IX.1 QUARTERLY TLD RESULTS FOR QUAD CITIES NUCLEAR POWER STATION, 2005 RESULTS IN UNITS OF MILLI-ROENTGEN/QUARTER +/- 2 STANDARD DEVIATIONS STATION MEAN JAN - MAR APR-JUN JUL-SEP OCT-DEC CODE +/- 2 S. D.

Q-201-1 22.8 +/- 6.6 26 19 21 25 Q-201-2 22.8 +/- 9.7 29 18 20 24 Q-202-1 20.8 +/- 8.2 26 16 20 21 Q-202-2 19.5 +/- 7.0 23 16 17 22 0-203-1 21.3 +/- 7.2 26 19 18 22 Q-203-2 25.8 +/- 8.5 31 21 24 27 Q-204-1 22.3 +/- 6.2 25 18 22 24 Q-204-2 24.3 +/- 7.0 26 20 23 28 Q-205-1 23.5 +/- 7.7 28 19 22 25 Q-205-4 24.3 +/- 6.6 28 21 22 26 Q-206-1 22.3 +/- 4.4 25 20 21 23 Q-206-2 22.0 +/- 8.5 25 17 20 26 Q-207-1 23.0 +/- 5.2 24 20 22 26 0-207-4 22.5 +/- 8.7 26 17 21 26 Q-208-1 22.3 +/- 9.1 27 17 20 25 Q-208-2 23.0 +/- 5.7 25 19 23 25 Q-209-1 22.3 +/- 10.1 28 18 (2) 43 (3)

Q-209-4 22.3 +/- 6.2 24 18 22 25 Q-210-1 21.8 +/- 7.5 25 19 18 25 Q-210-4 23.0 +/- 7.3 27 19 21 25 Q-211-1 26.0 +/- 9.9 31 20 24 29 Q-211-2 25.8 +/- 8.4 30 20 26 27 0-212-1 23.0 +/- 9.2 27 19 19 27 Q-212-2 20.3 +/- 7.7 23 16 18 24 Q-213-1 21.8 +/- 7.2 24 17 21 25 Q-213-2 21.3 +/- 7.7 25 17 19 24 0-214-1 22.5 +/- 8.2 25 19 19 27 0-214-2 24.5 +/- 5.3 25 22 23 28 Q-215-1 21.5 +/- 5.8 24 19 19 24 0-215-2 25.3 i 7.5 29 22 22 28 0-216-1 22.0 +/- 7.3 24 18 20 26 Q-216-2 23.8 +/- 8.5 27 18 23 27 (2) TLD NOT CHANGED (3) TLD WAS INSERVICE JULY THROUGH DECEMBER AND READ 43 MREM WHICH EQUALS AN AVERAGE OF 21.5 MREM/QUARTER C-16 91 of 206

TABLE C-IX.2 MEAN QUARTERLY TLD RESULTS FOR THE INNER RING, OUTER RING, OTHER AND CONTROL LOCATIONS FOR QUAD CITIES NUCLEAR POWER STATION, 2005 RESULTS IN UNITS OF MILLI-ROENTGEN/QUARTER +/- 2 STANDARD DEVIATIONS OF THE STATION DATA .

STATION INNER RING OUTER RING OTHER CONTROL CODE JAN-MAR 24.8 +/- 3.8 26.2 i 4.4 23.8 +/- 2.9 (1)

APR-JUN 17.1 +/-2.1 18.7 +/- 3.3 16.9 +/- 1.0 17.0 +/- 0.0 JUL-SEP 18.8 +/- 2.3 20.4 i 7.1 18.4 +/- 3.0 18.0 +/- 0.0 OCT-DEC 23.7 +/- 2.8 25.3 i 3.9 24.5 +/- 2.8 24.5 +/- 1.4 TABLE C-IX.3

SUMMARY

OF THE AMBIENT DOSIMETRY PROGRAM FOR QUAD CITIES NUCLEAR POWER STATION, 2005 RESULTS IN UNITS OF MILLI-ROENTGEN/QUARTER LOCATION SAMPLES PERIOD PERIOD PERIOD MEAN ANALYZED MINIMUM MAXIMUM

-

INNER RING 120 16 29 21.1 +/- 7.1 OUTER RING 126 16 31 22.8 +/- 7.3 OTHER 64 16 27 20.9 +/- 7.1 CONTROL 6 17 25 19.8 +/- 7.3 INNER RING STATIONS - Q-101-1, Q-101-2, Q-102-1, Q-102-3, Q-103-1, Q-103-2, Q-104-1, Q-104-2 Q-105-1, Q-105-2, 0-106-2, Q-106-3, 0-107-2, Q-107-3, Q-108-1, Q-108-2, Q-109-1, Q-109-2, Q-111-1 Q-111-2, Q-112-1, Q-112-2, Q-113-1, Q-113-2, Q-114-1, Q-114-2, Q-115-1, Q-115-2, Q-116-1, Q-116-2 OUTER RING STATIONS - Q-201-1, Q-202-2, Q-202-1, Q-202-2, Q-203-1, Q-203-2, Q-204-1, Q-204-2 Q-205-1, Q-205-4, Q-206-1, Q-206-2, 0-207-1, Q-207-4, Q-208-1, Q-208-2, Q-209-1, Q-209-4, Q-210-1, Q-210-4, Q-211-1, Q-211-2, Q-212-1, Q-212-2, Q-213-1, Q-213-2, 0-214-1, Q-214-2, Q-215-1, Q-215-2, Q-216-1, 0-216-2 OTHER STATIONS - Q-01-1, Q-01-2, Q-02-1, Q-02-2, Q-03-1, Q-03-2, Q-04-1, Q-04-2, Q-13-1, Q-13-2, Q-16-1, 0-16-2, Q-37-1, Q-37-2, Q-38-1, Q-38-2 CONTROL STATIONS - Q-07-1, Q-07-2 (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-17 92 of 206

TABLE C-X.1

SUMMARY

OF COLLECTION DATES FOR SAMPLES COLLECTED IN THE VICINITY OF QUAD CITIES NUCLEAR POWER STATION, 2005 SURFACE WATER (TRITIUM LIQUID SCINTILLATION)

COLLECTION PERIOD Q-33 Q-34 JAN-MAR 02/03/05 - 03/25/05 02/03/05 - 03/25/05 APR-JUN 04/04/05 - 07/01/05 04/04/05 07/01/05 JUL-SEP 07/08/05 - 09/30/05 07/08/05 - 09/30/05 OCT-DEC 10/07/05 - 12/30/05 10/07/05 - 12/30/05 SURFACE WATER (GROSS BETA & GAMMA SPECTROSCOPY)

COLLECTION PERIOD Q-33 Q-34 JAN (1) (1)

FEB 02/03/05 - 02/26/05 02/03/05 - 02/26/05 MAR 03/03/05 - 03/25/05 03/03/05 - 03/25/05 APR 04/04/05 - 04/29/05 04/04/05 - 04/29/05 MAY 05/05/05 - 05/27/05 05/05/05 - 05/27/05 JUN 06/02/05 - 07/01/05 06/02/05 - 07/01/05 JUL 07/08/05 - 07/29/05 07/08/05 - 07/29/05 AUG 08/05/05 - 08/26/05 08/05/05 - 08/26/05 SEP 09/02/05 - 09/30/05 09/02/05 - 09/30/05 OCT 10/07/05 - 10/28/05 10/07/05 - 10/28/05 NOV 11/03/05 - 11/25/05 11/03/05 - 11/25/05 DEC 12/02/05 - 12/30/05 12/02/05 - 12/30/05 GROUND WATER (TRITIUM & GAMMA SPECTROSCOPY)

COLLECTION PERIOD Q-35 0-36 JAN-MAR 01/14/05 01/14/05 APR-JUN 04/15/05 04/15/05 JUL-SEP 07/15/05 07/15/05 OCT-DEC 10/06/05 10/06/05 AIR PARTICULATE (GAMMA SPECTROSCOPY)

COLLECTION Q-01 0-02 Q-03 0-04 Q-07 PERIOD JAN-MAR 12/31/04 - 03/25/05 12/31/04 - 03/25/05 12/31/04 - 03/25/05 12/31/04 - 03/25/05 12/31/04 - 03/25/05 APR-JUN 03/25/05 - 07/02/05 03/25/05 - 07/02/05 03/25/05 - 07/02/05 03/25/05 - 07/02/05 03/25/05 - 07/01/05 JUL-SEP 07/02/05 - 09/30/05 07/02/05 - 09/30/05 07/02/05 - 09/30/05 07/02/05 - 09/30/05 07/02/05 - 09/30/05 OCT-DEC 09/30/05 - 12/30/05 09/30/05 - 12/30/05 09/30/05 - 12/30/05 09/30/05 - 12/30/05 09/30/05 - 12/30/05 AIR PARTICULATE (GAMMA SPECTROSCOPY)

COLLECTION 0-13 Q-16 Q-37 0-38 PERIOD JAN-MAR APR-JUN JUL-SEP 07/02/05 - 09/30/05 07/02/05 - 09/30/05 07/02/05 - 09/30/05 07/02/05 - 09/30/05 OCT-DEC 09/30/05 - 12/30/05 09/30/05 - 12/30/05 09/30/05 - 12/30/05 09/30/05 - 12/30/05 (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-18 93 of 206

SUMMARY

OF COLLECTION DATES FOR SAMPLES COLLECTED IN THE VICINITY OF QUAD CITIES NUCLEAR POWER STATION, 2005 AIR PARTICULATE (GROSS BETA & 1-131)

COLLECTION Q-01 Q-02 Q-03 Q-04 0-07 PERIOD 1 12131/04 -01/07/05 -- 12/31/04 - 01/07/05 12/31/04 - 01/07/05 12/31/04 -01107/05 12/31/04 - 01/07/05 2

01/07/05 - 01/14/05 01/07/05 - 01/14/05 01/07/05 - 01/14/05 01/07/05 -01/14/05 01/07/05 - 01/14/05 3 01/14/05 - 01/21/05 01/14/05 - 01/21/05 01/14/05 - 01/21/05 01/14/05 -01/21/05 01/14/05 - 01/21/05 4

01/21/05 - 01/28/05 01/21/05 - 01/28/05 01/21/05 - 01/28/05 01/21/05 -01/28/05 01/21/05 - 01/28/05 5 01/28/05 - 02104/05 01/28/05 - 02104/05 01/28/05 - 02104/05 01/28/05 -02/04/05 01/28/05 - 02/04/05 6

02/04/05 - 02/11/05 02/04/05 - 02/11/05 02/04/05 - 02/11/05 02/04/05 -02/11/05 02/04/05 - 02/11/05 7 02/11/05 - 02/18/05 02/11/05 - 02/18/05 02/11/05 - 02/18/05 02/11/05 -02/18/05 02/11/05 - 02/18/05 8

02/18/05 - 02/26/05 02/18/05 - 02/26/05 02/18/05 - 02/26/05 02/18/05 -02/26/05 02/18/05 - 02/26/05 9 02/26/05 - 03/04/05 02/26/05 - 03/04/05 02/26/05 - 03/04/05 02/26/05 -03/04/05 02/26/05 - 03/04/05 10

03/04/05 - 03/11/05 03/04/05 - 03/11/05 03/04/05 - 03/11/05 03/04/05 -03/11/05 03/04/05 - 03/10/05 11 03/11/05 - 03/18/05 03/11/05 - 03/18/05 03/11/05 - 03/18/05 03/11/05 -03/18/05 03/10/05 - 03/18/05 12

03/18/05 - 03/25/05 03/18/05 - 03/25/05 03/18/05 - 03/25/05 03/18/05 -03/25/05 03/18/05 - 03/25/05 13 03/25/05 - 04/02/05 03/25/05 - 04/02/05 03/25/05 - 04/02/05 03/25105 -04/02/05 03/25/05 - 04/01/05 14

04/02/05 - 04/08/05 04/02/05 - 04/08/05 04/02/05 - 04/08/05 04/02/05 -04/08/05 04/01/05 - 04/08/05 15 04/08/05 - 04/15/05 04/08/05 - 04/15/05 04/08/05 - 04/15/05 04/08/05 -04/15/05 04/08/05 - 04/15/05 16

04/15/05 - 04/22/05 04/15/05 - 04/22/05 04/15/05 - 04/22/05 04/15/05 -04/22/05 04/15/05 - 04/22/05 17 04/22/05 - 04/29/05 04/22/05 - 04/29/05 04/22/05 - 04/29/05 04/22/05 -04/29/05 04/22/05 - 04/29/05 18

04/29/05 - 05/06/05 04/29/05 - 05/06/05 04/29/05 - 05/06/05 04/29/05 -05/06/05 04/29/05 - 05/06/05 19 05/06/05 - 05/13/05 05/06/05 - 05/13/05 05/06/05 - 05/13/05 05/06/05 -05/13/05 05/06/05 - 05/13/05 20

05/13/05 - 05/20/05 05/13/05 - 05/20/05 05/13/05 - 05/20/05 05/13/05 -05/20/05 05/13/05 - 05/20/05 21 05/20/05 - 05/27/05 05/20/05 - 05/27/05 05/20/05 - 05/27/05 05/20/05 -05/27/05 05/20/05 - 05/27/05 22

05/27/05 - 06/03/05 05/27/05 - 06/03/05 05/27/05 - 06/03/05 05/27/05 -06/03/05 05/27/05 - 06/03/05 23 06/03/05 - 06/11/05 06/03/05 - 06/11/05 06/03/05 - 06/11/05 06/03/05 -06/11/05 06/03/05 - 06/09/05 24

06/11/05 - 06/17/05 06/11/05 - 06/17/05 06/11/05 - 06/17/05 06/11/05 -06/17/05 06/09/05 - 06/17/05 25 06/17/05 - 06/24/05 06/17/05 - 06/24/05 06/17/05 - 06/24/05 06/17/05 -06/24/05 06/17/05 - 06/24/05 26

06/24/05 - 07/02/05 06/24/05 - 07/02/05 06/24/05 - 07/02/05 06/24/05 -07/02/05 06/24/05 - 07/01/05 27 07/02/05 - 07/08/05 07/02/05 - 07/08/05 07/02/05 - 07/08/05 07/02/05 -07/08/05 07/02/05 - 07/08/05 28

07/08/05 - 07/15/05 07/08/05 - 07/15105 07/08/05 - 07/15/05 07/08/05 -07/15/05 07/08/05 - 07/15/05 29 07115/05 - 07/22/05 07/15/05 - 07/22/05 07/15/05 - 07/22/05 07/15/05 -07/22/05 07/15/05 - 07/22/05 30

07/22/05 - 07/29/05 07/22/05 - 07/29/05 07/22/05 - 07/29/05 07/22/05 -07/29/05 07/22/05 - 07/29/05 31 07/29/05 - 08/05/05 07/29/05 - 08/05/05 07/29/05 - 08/05/05 07/29/05 -08/05/05 07/29/05 - 08/05/05 32

08/05/05 - 08/12105 08/05/05 - 08/12/05 08/05/05 - 08/12105 08/05/05 -08/1205 08/05/05 - 08/12/05 33 08/12/05 - 08/19/05 08/12/05 - 08/19/05 08/12/05 - 08/19/05 08/12/05 -08/19/05 08/12/05 - 08/19/05 34

08/19/05 - 08/26/05 (1) 08/19/05 - 08/26/05 08/19/05 -08/26/05 08/19/05 - 08/26/05 35 08/26/05 - 09/02/05 08/26/05 - 09/02/05 08/26/05 - 09/02/05 08/26/05 -09/02/05 08/26/05 - 09/02/05 36

09/02/05 - 09/09/05 09/02/05 - 09/09/05 09/02/05 - 09/09/05 09/02/05 -09/09/05 09/02/05 - 09/09/05 37 09/09/05 - 09/16/05 09/09/05 - 09/16/05 09/09/05 - 09/16/05 09/09/05 -09/16/05 09/09/05 - 09/16/05 38

09/16/05 - 09/23/05 09/16/05 - 09/23/05 09/16/05 - 09/23/05 09/16/05 -09/23/05 09/16/05 - 09/23/05 39 09/23/05 - 09/30/05 09/23/05 - 09/30/05 09/23/05 - 09/30/05 09/23/05 -09/30/05 09/16/05 - 09/23/05 40

09/30/05 - 10/07/05 09/30/05 - 10/07/05 09/30/05 - 10/07/05 09/30/05 -10/07/05 09/23/05 - 09/30/05 41 (1) 10/07/05 - 10/14/05 10/07/05 - 10/14/05 09/30/05 -10/07/05 09/30/05 - 10/07/05 42 (1) 10/14/05 - 10/21/05 10/14/05 - 10/21/05 10/07/05 -10/14/05 10/07/05 - 10/14/05 43 10/21105 - 10/28/05 10/21/05 - 10/28/05 10/14/05 - 10/21/05 10/14/05 -10/21/05 10/14/05 - 10/21/05 44

10/28/05 - 11/04/05 10/28/05 - 11/04/05 10/21/05 - 10/28/05 10/21/05 -10/28/05 10/21/05 - 10/28/05 45 11/04/05 - 11/11/05 11/04/05 - 11/11/05 10/28/05 - 11/04/05 10/28/05 -11/04/05 10/28/05 - 11/03/05 46

11/11/05 - 11/18/05 11/11/05 - 11/18/05 11/04/05 - 11/11/05 11/04/05 -11/11/05 11/03/05 - 11/11/05 47 11/18/05 - 11/25/05 11/11/05 - 11/18/05 11/11/05 - 11/18/05 11/11/05 -11/18/05 11/11/05 - 11/18/05 48

11/25/05 - 12/02/05 11/18/05 - 11/25/05 11/18/05 - 11/25/05 11/18/05 -11/25/05 11/18/05 - 11/25/05 49 12/02/05 - 12/09/05 11/25/05 - 12/02/05 11/25/05 - 12/02/05 11/25/05 -12/02/05 11/25/05 - 12/02/05 50

12/09/05 - 12/16/05 12/02/05 - 12/09/05 12/02/05 - 12/09/05 12/02/05 -12/09/05 12/02/05 - 12/09/05 51 12/16/05 - 12/23/05 12/16/05 - 12/23/05 12116/05 - 12/23/05 12/16/05 -12/23/05 12/16/05 - 12/23/05 52

12/23/05 - 12/30/05 12/23/05 - 12/30/05 12/23/05 - 12/30/05 12/23/05 -12/30/05 12/23/05 - 12/30/05

AIR IODINE SAMPLES COLLECTED BIWEEKLY (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-19 94 of 206

TABLE C-X.1

SUMMARY

OF COLLECTION DATES FOR SAMPLES COLLECTED IN THE VICINITY OF QUAD CITIES NUCLEAR POWER STATION, 2005 AIR PARTICULATE (GROSS BETA & 1-131)

COLLECTION Q-13 Q-16 Q-37 Q-38 PERIOD 1 12/31/04 - 01/07/05 12/31/04 - 01/07/05 12/31/04 - 01/07/05 12/31/04 - 1/r7/05 2 01/07/05 - 01/14/05 01/07/05 - 01/14/05 01/07/05 - 01/14/05 01/07/05 - 01/14/05 3 01/14/05 - 01/21/05 01/14/05 - 01/21/05 01/14/05 - 01/21/05 01/14/05 - 01/21/05 4

01/21/05 - 01/28/05 01/21/05 - 01/28/05 01/21/05 - 01/28/05 01/21/05 - 01/28/05 5 01/28/05 - 02/04/05 01/28/05 - 02/04/05 01/28/05 - 02/04/05 01/28/05 - 02/04/05 6 02/04/05 - 02/11/05 02/04/05 - 02/11/05 02/04/05 - 02/11/05 02/04/05 - 02/11/05 7 02/11/05 - 02/18/05 02/11/05 - 02/18/05 02/11/05 - 02/18/05 02/11/05 - 02/18/05 8

02/18/05 - 02/26/05 02/18/05 - 02/26/05 02/18/05 - 02/26/05 02/18/05 - 02/26/05 9 02/26/05 - 03/04/05 02/26/05 - 03/04/05 02/26/05 - 03/04/05 02/26/05 - 03/04/05 10

03/04/05 - 03/10/05 03/04/05 - 03/10/05 03/04/05 - 03/11/05 03/04/05 - 03/11/05 11 03/10/05 - 03/18/05 03/10/05 - 03/18/05 03/11/05 - 03/18/05 03/11/05 - 03/18/05 12

03/18/05 - 03/25/05 03/18/05 - 03/25/05 03/18/05 - 03/25/05 03/18/05 - 03/25/05 13 03/25/05 - 04/01/05 03/25/05 - 04/01/05 03/25/05 - 04/02/05 03/25/05 - 04/02/05 14

04/01/05 - 04/08/05 04/01/05 - 04/08/05 04/02/05 - 04/08/05 04/02/05 - 04/08/05 15 04/08/05 - 04/15/05 04/08/05 - 04/15/05 04/08/05 - 04/15/05 04/08/05 - 04/15/05 16

04/15/05 - 04/22/05 04/15/05 - 04/22/05 04/15/05 - 04/22/05 04/15/05 - 04/22/05 17 04/22/05 - 04/29/05 04/22/05 - 04/29/05 04/22/05 - 04/29/05 04/22/05 - 04/29/05 18 ^ 04/29/05 - 05/06/05 04/29/05 - 05/06/05 04/29/05 - 05/06/05 04/29/05 - 05/06/05 19 05/06/05 - 05/13/05 05/06/05 - 05/13/05 05/06/05 - 05/13/05 05/06/05 - 05/13/05 20

05/13/05 - 05/20/05 05/13/05 - 05/20/05 05/13/05 - 05/20/05 05/13/05 - 05/20/05 21 05/20/05 - 05/27/05 05/20/05 - 05/27/05 05/20/05 - 05/27/05 05/20/05 - 05/27/05 22

05/27/05 - 06/03/05 05/27/05 - 06/03/05 05/27/05 - 06/03/05 05/27/05 -06/03/05 23 06/03/05 - 06/09/05 06/03/05 - 06/09/05 06/03/05 - 06/11/05 06/03/05 - 06/11/05 24

06/09/05 - 06/17/05 06/09/05 - 06/17/05 06/11/05 - 06/17/05 06/11/05 - 06/17/05 25 06/17/05 - 06/24/05 06/17/05 - 06/24/05 06/17/05 - 06/24/05 06/17/05 - 06/24/05 26

06/24/05 - 07/01/05 06/24/05 - 07/01/05 06/24/05 - 07/02/05 06/24/05 - 07/02/05 27 07/01/05 - 07/08/05 07/01/05 - 07/08/05 07/02/05 - 07/08/05 07/02/05 - 07/08/05 28 t 07/08/05 - 07/15/05 07/08/05 - 07/15/05 07/08/05 - 07/15/05 07/08/05 - 07/15/05 29 07/15/05 - 07/22/05 07/15/05 - 07/22/05 07/15/05 - 07/22/05 07/15/05 - 07/22/05 30

07/22/05 - 07/29/05 07/22/05 - 07/29/05 07/22/05 - 07/29/05 07/22/05 - 07/29/05 31 07/29/05 - 08/05/05 07/29/05 - 08/05/05 07/29/05 - 08/05105 07/29/05 - 08/05/05 32

08/05/05 - 08/12/05 08/05/05 - 08/12/05 08/05/05 - 08/12/05 08/05/05 - 08/12/05 33 08/12/05 - 08/19/05 08/12/05 - 08/19/05 08/12/05 - 08/19/05 08/12/05 - 08/19/05 34

08/19/05 - 08/26/05 08/19/05 - 08/26/05 08/19/05 - 08/26/05 08/19/05 - 08/26/05 35 08/26/05 - 09/02/05 08/19/05 - 08/26/05 08/19/05 - 08/26/05 08/19/05 - 08/26/05 36

09/02/05 - 09/09/05 08/26/05 - 09/02/05 08/26/05 - 09/02/05 08/26/05 - 09/02/05 37 09/09/05 - 09/16/05 09/09/05 - 09/16/05 09/09/05 - 09/16/05 09/09/05 - 09/16/05 38

09/16/05 - 09/23/05 09/16/05 - 09/23/05 09/16/05 - 09/23/05 09/16/05 - 09/23/05 39 09/23/05 - 09/30/05 09/23/05 - 09/30/05 09/23/05 - 09/30/05 09/23/05 - 09/30/05 40

09/30/05 - 10/07/05 09/30/05 - 10/07/05 09/30/05 - 10/07/05 09/30/05 - 10/07/05 41 10/07/05 - 10/14/05 10/07/05 - 10/14/05 10/07/05 - 10/14/05 10/07/05 - 10/14/05 42 ^ 10/14/05 - 10/21/05 10/14/05 - 10/21/05 10/14/05 - 10/21/05 10/14/05 - 10/21/05 43 10/21/05 - 10/28/05 10/21/05 - 10/28/05 10/21/05 - 10/28/05 10/21/05 - 10/28/05 44 ' 10/28/05 - 11/03/05 10/28/05 - 11/03/05 10/28/05 - 11/03/05 10/28/05 - 11/03/05 45 11/03/05 - 11/11/05 11/03/05 - 11/11/05 11/03/05 - 11/11/05 11/03/05 - 11/11/05 46

11/11/05 - 11/18/05 11/11/05 - 11/18/05 11/11/05 - 11/18/05 11/11/05 - 11/18/05 47 11/18/05 - 11/25/05 11/18/05 - 11/25/05 11/18/05 - 11/25/05 11/18/05 - 11/25/05 48 ^ 11/25/05 - 12/02/05 11/25/05 - 12/02/05 11/25/05 - 12/02/05 11/25/05 - 12/02/05 49 12/02/05 - 12/09/05 12/02/05 - 12/09/05 12/02/05 -12/09/05 12/02/05 - 12/09/05 50

12/09/05 - 1216/05 12/09/05 - 12/16/05 12/09/05 -1216/05 12/09/05 - 12/16/05 51 12/16/05 - 1223/05 12/16/05 - 12/23/05 12/16/05 -12/23/05 12/16/05 - 12/23/05 52

12/23/05 - 12/30/05 12/23/05 - 12/30/05 12/23/05 -12/30/05 12/23/05 - 12/30/05

AIR IODINE SAMPLES COLLECTED BIWEEKLY C-20 95 of 206

TABLE C-X.1

SUMMARY

OF COLLECTION DATES FOR SAMPLES COLLECTED IN THE VICINITY OF QUAD CITIES NUCLEAR POWER STATION, 2005 TLD STATION JAN - MAR APR - JUN JUL - SEP OCT - DEC CODE Q-01 -1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-01-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-02-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-02-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-03-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-03-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-04-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-04-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 0-13-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-13-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-16-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-16-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-37-1 01/01/05 - 04/01/05 04/01/05 -07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-37-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 0-38-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-38-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-101-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-101-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 10/01/05 10/01/05 - 01/01/06 Q-102-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-102-3 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-103-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-103-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-104-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-104-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-105-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-105-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-106-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-106-3 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-107-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-107-3 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-108-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 0-108-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-109-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-109-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-111-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-111-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-112-1 01/01/05 - 04/01105 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01106 Q-112-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-113-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-113-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-114-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-114-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-115-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-115-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-116-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-116-3 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 C-21 96 of 206

TABLE C-X.1

SUMMARY

OF COLLECTION DATES FOR SAMPLES COLLECTED IN THE VICINITY OF QUAD CITIES NUCLEAR POWER STATION, 2005 TLD STATION JAN - MAR APR - JUN JUL - SEP OCT - DEC CODE Q-201 -1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-201-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-202-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05- 10/01/05 10/01/05 - 01/01/06 Q-202-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05- 10/01/05 10/01/05 - 01/01/06 Q-203-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-203-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 0-204-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-204-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-205-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-205-4 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-206-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-206-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-207-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-207-4 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-208-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05- 10/01/05 10/01/05 - 01/01/06 0-208-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05- 10/01/05 10/01/05 - 01/01/06 0-209-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-209-4 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05- 10/01/05 10/01/05 - 01/01/06 Q-210-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-210-4 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05- 10/01/05 10/01/05 - 01/01/06 Q-211-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-211-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-212-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-212-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-213-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-213-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-214-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 0-214-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-215-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-215-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 0-216-1 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 Q-216-2 01/01/05 - 04/01/05 04/01/05 - 07/01/05 07/01/05 - 10/01/05 10/01/05 - 01/01/06 C-22 97 of 206

FIGURE C-1 Surface Water - Gross Beta - Stations Q-33 and Q-34 (C)

Collected in the Vicinity of QCNPS, 2000 - 2004 Q-33 Cordova 12.0 10.0 8.0 4.0 2.0 0.0 -

01-01-00 12-31-00 12-31-01 12-31-02 12-31-03 12-30-04 Q-34 (C) Camanche 10.0 01-01-00 12-31-00 12-31-01 12-31-02 12-31-03 12-30-04 98 of 206

FIGURE C-1 (cont.)

Surface Water - Gross Beta - Stations Q-33 and Q-34 (C)

Collected in the Vicinity of QCNPS, 2005 Q-33 Cordova 12.0 T-10.0 +

-J 6.0 +

4.0 +

2.0 -

0.0 12-01-04 02-01-05 04-01-05 06-01-05 081-05 10-01-05 12-01-05 Q-34 Camanche 12.0 ,-

10.0 +

c.

U 6.0 4 2.0.

0.0 I I I I I 12-01-04 02-01-05 04-01-05 06-01-05 08-01-05 10-01-05 12-01-05 DUE TO VENDOR CHANGE, < VALUES ARE LLD VALUES JANUARY THROUGH JUNE AND MDC VALUES JULY THROUGH DECEMBER 99 of 206

FIGURE C-2 Surface Water - Tritium - Stations Q-33 and Q-34 (C)

Collected in the Vicinity of QCNPS, 2000 - 2004 Q-33 Cordova 500 o

A IS 4Wu 300

-J 200 0.

100

-100 ~-

01-01-00 12-31-00 12-31-01 12-31-02 12-31-03 12-30-04 Q-34 (C) Camanche 500 0 400 +

300 +

-i 200 +

0.

100 +

0+

-100]-- I I 01-01-00 12-31-00 12-31-01 12-31-02 12-31-03 12-30-04 100 of 206

FIGURE C-2 (cont.)

Surface Water - Tritium - Stations Q-33 and Q-34 (C)

Collected in the Vicinity of QCNPS, 2005 Q-33 Cordova 500 -

400].

300 -I.

YJ 200 + 0 100 +

0 d 03-31-05 06-30-05 09-30-05 12-31 -05 Q-34 (C) Camanche 500 -r 400-300-C)

C.

200- 0 100.

0r 03-31-05 06-30-05 09-30-05 12-31-05 DUE TO VENDOR CHANGE, <VALUES ARE LLD VALUES JANUARY THROUGH JUNE AND MDC VALUES JULY THROUGH DECEMBER 101 of 206

FIGURE C-3 Ground Water - Tritium - Stations Q-35 and Q-36 Collected in the Vicinity of QCNPS, 2000 - 2004 Q-35 McMillan Well 500 400 300 200 0~

la 100 \/ /

-100

-200 I Ii . I ,

01-01-00 12:31-00 12-31-0-1 12-31-02 12-31403 12-300-04 Q-36 Cordova Well 500 400 300 200 4.

100

-100

-200 i I I I l l

01-01-00 12-31-00 12-31-01 12-31-02 12-31-03 12-30-04 102 of 206

FIGURE C-3 (cont.)

Ground Water - Tritium - Stations Q-35 and Q-36 Collected in the Vicinity of QCNPS, 2005 Q-35 McMillan Well 500 ,-

400 +

300 -.

X1 a.

200 +

100 +

0 I I 03-01-05 06-01-05 09-01-05 12-01-05 Q-36 Cordova Well 500 T 400 -.-

300 .-

-j Q

a.

200 +

100 +

0 03-01-05 06-01-05 09-01-05 12-01-05 DUE TO VENDOR CHANGE, <VALUES ARE LLD VALUES JANUARY THROUGH JUNE AND MDC VALUES JULY THROUGH DECEMBER 103 of 206

FIGURE C-4 Air Particulates - Gross Beta- Stations Q-01 and Q-02 Collected in the Vicinity of QCNPS, 2000 - 2004 Q-01 Onsite No. i 10.01 80 CO 2,0 0.0 01-01-00 12.31-00 12-31-01 12 t2-3143 12-30-04 Q-02 Onsite No. 2 10.0 8.0k-2.01 t~a/

00, '

010140 12-31-00 1241-01 12-31-02 12-31-03 12-30.04 104 of 206

FIGURE C-4 (cont.)

Air Particulates - Gross Beta- Stations Q-01 and Q-02 Collected in the Vicinity of QCNPS, 2005 Q-01 Onsite No. I 60.0 T 50.0 4 E 40.0 4 30.0 4 CL 119 us v- 20.0 4 10.0.

0.0.0 a 12-31-04 02-28-05 04-30-05 06-30-05 08-31-05 10-31-05 12-3' 1-05 Station 0-01 lost power 10-07 10-21-05.

Q-02 Onsite No. 2 60.0 -r 50.0.

40.0*

a.

30.0 -1.

9 III CD 20.0 +

10.0-0.0 4-0 12-31-04 02-28-05 04-30-05 06-30-05 08-31-05 10-31-05 12-31-05 Station 0-02 lost power 08-19 08-26-05.

DUE TO VENDOR CHANGE, THE REPORTED UNITS CHANGED FROM E-02 PCI/M3 TO E-03 PCI/M3 105 of 206

FIGURE C-5 Air Particulates - Gross Beta- Stations Q-03 and Q-04 Collected in the Vicinity of QCNPS, 2000 - 2004 Q-03 Onsite No. 3 10.0 1 8.0 -1 6.0 I4 4.0 2.0 IVQ5 I 0.0 I 01-01-00 12-31-00 12-31-01 12-31-02 12-31-03 12-30-04 Q-04 Nitrin 10.0 .

8.0 -

6.0-I v.

4.0-2.01

,!I -,

01-0 1O00 12-31-00 12-31-01 12-31-02 12-31-03 12-30-04 106 of 206

FIGURE C-5 (cont.)

Air Particulates - Gross Beta- Stations Q-03 and Q-04 Collected in the Vicinity of QCNPS, 2005 Q-03 Onsite No. 3 60.0.

50.0 .

40.0 CL 30.0--

9 20.0 -

10.0 12-31-04 02-28-05 04-30-05 06-30-05 08-31-05 10-31-05 12-31-05 Q-04 Nitrin 60.0 50.0 40.0 30.0 9

'U 20.0 10.0 o0o-12-31-04 02-28-05 04-30-05 06-30-05 08-31-05 10-31-05 12-31-05 DUE TO VENDOR CHANGE, THE REPORTED UNITS CHANGED FROM E-02 PCI/M3 TO E-03 PCI/M3 107 of 206

FIGURE C-6 Air Particulates - Gross Beta- Stations Q-07 (C)

Collected in the Vicinity of QCNPS, 2000 - 2004 Q-07 (C) Clinton 10.0 8E,0]

a,

e. 40Ai 0.0 01-0i.O0 12.31-00 12-31-01 12-31-02 12-31-03 12-30.04 108 of 206

FIGURE C-6 (cont.)

Air Particulates - Gross Beta- Stations Q-07 (C)

Collected in the Vicinity of QCNPS, 2005 Q-07 (C) Clinton 60.0 ,-

50.0 +

E 40.0+

-

5

,,, 30.0

°2.

9 0 20.0 10.0.

0.01 s t i I 12-31-04 02-28-05 04-30-05 06-30-05 08-31-05 10-31-05 12-31-05 DUE TO VENDOR CHANGE, THE REPORTED UNITS CHANGED FROM E-02 PCI/M3 TO E-03 PCI/M3 109 of 206

FIGURE C-7 Air Particulates - Gross Beta- Stations Q-13 and Q-16 Collected in the Vicinity of QCNPS, 2005 Q-13 Princeton 60.0 -

50.0 +

40.0 *4.

Ua.

30.0 +

cI C?

of 20.0 .4 10.0 12-31 -04 02-28-05 04-30-05 06-30-05 08-31-05 10-31-05 12-31-05 Q-13 Princeton 60.0 ,-

50.0 -.

40.0 +

30.0 -

20.0 10.0 -

tin p 12-31-04 02-28-05 04-30-05 06-30-05 08-31-05 10-31-05 12-31-05 DUE TO VENDOR CHANGE, THE REPORTED UNITS CHANGED FROM E-02 PCIIM3 TO E-03 PCI/M3 AIR PARTICULATE GROSS BETA ANALYSES OF FAR FIELD LOCATIONS STARTED INJULY 2005 110 of 206

FIGURE C-8 Air Particulates - Gross Beta- Stations Q-37 and Q-38 Collected in the Vicinity of QCNPS, 2005 Q-37 Meredosia Road 60.0 -r 50.0 40.0 30.0 +

rb CL 9o 20.0 +

10.0*

0n I.

12-31 -04 02-28-05 04-30-05 06-30-05 08-31-05 10-31-05 12-31-05 Q-38 Fuller Road 60.0 T 50.0 +

m 40.0 +

30.0 +

9 Uj

!9 20.0 +

10.0 +

0.0 I- 0 0 0 . 1 12-31-04 02-28-05 04-30-05 06-30-05 08-31-05 10-31-05 12-31-05 DUE TO VENDOR CHANGE, THE REPORTED UNITS CHANGED FROM E-02 PCI/M3 TO E-03 PCI/M3 AIR PARTICULATE GROSS BETA ANALYSES OF FAR FIELD LOCATIONS STARTED INJULY 2005 111 of 206

APPENDIX D INTER-LABORATORY COMPARISON PROGRAM 112 of 206

TABLE D-1 ANALYTICS ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING, 2005 (PAGE 1 OF 3)

Identification Reported Known Ratio (c)

Month/Year Number Matrix Nuclide Units Value (a) Value (b) TBE/Analytics Evaluation (d)

March 2005 E4522-396 Milk Sr-89 pCi/L 96.9 107 0.91 Sr-90 pCi/L 16.9 17.9 0.94 E4523-396 Milk 1-131 pCi/L 82.7 92.3 0.90 Ce-141 pCi/L 217 229 0.95 Cr-51 pCi/L 314 334 0.94 Cs-134 pCi/L 123 139 0.89 Cs-1 37 pCi/L 125 130 0.96 Co-58 pCi/L 110 115 0.96 Mn-54 pCi/L 158 160 0.99 Fe-59 pCi/L 118 111 1.06 Zn-65 pCi/L 191 198 0.96 Co-60 pCi/L 140 144 0.97 E4525-396 AP Ce-141 pCi 150 172 0.87 Cr-51 pCi 278 250 1.11 Cs-134 pCi 105 104 1.01 Cs-1 37 pCi 95.6 97.1 0.98 Co-58 pCi 84.4 86.3 0.98 Mn-54 pCi 112 120 0.93 Fe-59 pCi 92.8 83.2 1.12 Zn-65 pC! 162 148 1.09 Co-60 pCi 102 108 0.94 E4524-396 Charcoal 1-131 pCi 67.4 60.7 1.11 June 2005 E4630-396 Milk Sr-89 pCi/L 89.4 88.1 1.01 A Sr-90 pCi/L 11.6 11.4 1.02 A E4631-396 Milk 1-131 pCi/L 82.3 86.9 0.95 A Ce-1 41 pCi/L 91.6 92.4 0.99 A Cr-51 pCi/L 278 303 0.92 A Cs-134 pCi/L 81.1 95.0 0.85 A Cs-137 pCi/L 180 189 0.95 A Mn-54 pCi/L 124 125 0.99 A Fe-59 pCi/L 61.1 63.9 0.96 A Zn-65 pCi/L 156 155 1.01 A Co-60 pCi/L 136 145 0.94 A E4633-396 AP Ce-141 pCi 79.2 64.2 1.23 w Cr-51 pCi 263 210 1.25 W Cs-134 pC! 69.7 66.1 1.05 A Cs-137 pCi 135 131 1.03 A Mn-54 pCi 94.9 87.0 1.09 A Fe-59 pCi 48 44.4 1.09 A Zn-65 pCi 120 108 1.11 A Co-60 pCi 104 101 1.03 A E4632-396 Charcoal 1-131 pCi 88.9 92.5 0.96 A D-1 113 of 206

TABLE D-1 ANALYTICS ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING, 2005 (PAGE 2 OF 3)

Identification Reported Known - Ratio (c)

Month/Year Number Matrix Nuclide Units Value (a) Value (b) TBE/Analytics Evaluation (d)

September 2005 E4766-396 Milk Sr-89 pCi/L 135.0 146.0 0.92 A Sr-90 pCi/L 9.7 11.5 0.84 A E4767-396 Milk 1-131 pCi/L 87.5 94.3 0.93 A Ce-141 pCi/L 203 233 0.87 A Cr-51 pCi/L 279 338 0.83 A Cs-134 pCi/L 102 122.0 0.84 A Cs-1 37 pCi/L 178 195 0.91 A Co-58 pCi/L 55.3 63.4 0.87 A Mn-54 pCi/L 81.8 92.0 0.89 A Fe-59 pCi/L 59.9 61.0 0.98 A Zn-65 pCi/L 120 123 0.98 A Co-60 pCi/L 146 167 0.87 A E4769-396 AP Ce-141 pci 193 169 1.14 A Cr-51 pci 267 246 1.09 A Cs-134 pci 78.4 88.8 0.88 A Cs-137 pci 166 142 1.17 A Co-58 pC 53.7 46.0 1.17 A Mn-54 pC 81.6 66.8 1.22 W Fe-59 pC 59.6 44.3 1.35 N (1)

Zn-65 pci 107 89.6 1.19 A Co-60 pci 133 122 1.09 A E4768-396 Charcoal 1-131 pCi 63.9 64.2 1.00 A December 2005 E4766-396 Milk Sr-89 pCi/L 114 128 0.89 A Sr-90 pCi/L 11.6 10.3 1.13 A E4767-396 Milk 1-131 pCi/L 79.6 74.6 1.07 A Ce-141 pCi/L 202 224 0.90 A Cr-51 pCi/L 185 193 0.96 A Cs-134 pCi/L 74.9 87.3 0.86 A Cs-137 pCi/L 177 189 0.94 A Co-58 pCi/L 73.9 77.5 0.95 A Mn-54 pCi/L 152 152 1.00 A Fe-59 pCi/L 97.5 82.4 1.18 A Zn-65 pCi/L 161 154 1.05 A Co-60 pCi/L 102 ill 0.92 A E4633-396 AP Ce-141 pCi 221 201 1.10 A Cr-51 pCi 195 173 1.13 A Cs-134 pCi 68.4 78.3 0.87 A

Cs-137 pCi 194 170 1.14 A Co-58 pCi 77.4 69.4 1.12 A Mn-54 pCi 171 137 1.25 W Fe-59 pCi 94.2 73.9 1.27 W Zn-65 pCi 173 138 1.25 W Co-60 pCi 109 99.1 1.10 A D-2 114 of 206

TABLE D-1 ANALYTICS ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING, 2005 (PAGE 3 OF 3)

Identification Reported Known Ratio (c)

Month/Year Number Matrix Nuclide Units Value (a) Value (b) TBE/Analytics Evaluation (d)

December 2005 E4632-396 Charcoal 1-131 pCi 73.3 73.3 1.00 A (1) New technician -APnotcountedin peti dish resultedin high Fe-59 activity Countingin petridish, the Fe-59 wouldhave been acceptable as evidenced by the 4Q05 AP recount data. NCR 06-01 (a) Teledyne Brown Engineering reported result.

(b) The Analytics known value is equal to 100% of the parameter present in the standard as determined by gravimetric and/or volumetric measurements made during standard preparation.

(c) Ratio of Teledyne Brown Engineering to Analytics results.

(d) Analytics evaluation based on TBE internal OC limits: A= Acceptable. Reported result falls within ratio limits of 0.80-1.20.

W-Acceptable with warning. Reported result falls within 0.70-0.80 or 1.20-1.30. N = Not Acceptable. Reported result falls outside the ratio limits of < 0.70 and > 1.30.

D-3 115 of 206

TABLE D-2 ERA ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING, 2005 (PAGE t OF 1)

Identification Reported Known Month/Year Number Media Nuclide Units Value (a) Value (b) Control Limits Evaluation (c)

May 2005 Rad 61 Water Sr-89 pCi/L 37.5 41.3 32.6 - 50.0 A Sr-90 pCi/L 5.37 5.92 0.00 - 14.6 A Ba-1 33 pCi/L 88.6 88.4 73.1 - 104 A Cs-134 pCi/L 70.5 78.6 69.9 - 87.3 A Cs-137 pCi/L 201 201 184 - 218 A Co-60 pCi/L 37.5 37.0 28.3 - 45.7 A Zn-65 pCi/L 122 118 97.6- 138 A Gr-A pCi/L 35.5 37.0 21.0 - 53.0 A Gr-B pCi/L 35.6 34.2 25.5 - 42.9 A H-3 pCi/L 24600 24400 20200 - 28600 A Rad 61 Water 1-131 pCi/L 13.6 15.5 10.3 - 20.7 A November 2005 Rad 63 Water Sr-89 pCi/L 18.0 19.0 10.3 - 27.7 A Sr-90 pCi/L 16.6 16.0 7.37 - 24.7 A Ba-133 pCi/L 31.7 31.2 22.5 - 39.9 A Cs-134 pCi/L 30.8 33.9 25.2 - 42.6 A Cs-1 37 pCi/L 26.8 28.3 19.6 - 37.0 A Co-60 pCi/L 83.9 84.1 75.4 - 92.8 A Zn-65 pCi/L 109 105 86.8 - 123 A Gr-A pCi/L 19.5 23.3 13.2 - 33.4 A Gr-B pCi/L 34.0 39.1 30.4 - 47.8 A H-3 pCi/L 12400 12200 10100 - 14300 A Rad 63 Water 1-131 pCi/L 17.8 17.4 12.2 - 22.6 A (a) Teledyne Brown Engineering reported result.

(b) The ERA known value is equal to 1O0°h of the parameterpresent in the standard as determined by gravimetric and/or volumetric measurements made during standard preparation.

(c) ERA evaluation: A=acceptable. Reported result falls within the Warning Limits. NA=not acceptable. Reported result falls outside of the Control Limits. CE=check for Error. Reported result falls within the Control Limits and outside of the Warning Limit.

D-4 116 of 206

TABLE D-3 DOE'S MIXED ANALYTE PERFORMANCE EVALUATION PROGRAM (MAPEP)

TELEDYNE BROWN ENGINEERING, 2005 (PAGE 1 OF 2)

Identification Reported Known Acceptance Month/Year Number Media Nuclide Units Value (a) Value (b) Range Evaluation (c)

April 2005 05-MaW13 Water Cs-134 Bq/L 108 127 88.90 - 165.10 Cs-137 Bq/L 305 332 232.40 - 461.60 Co-57 Bq/L 215 227 158.90 - 295.10 Co-60 Bq/L 241 251 175.70 - 326.30 H-3 Bq/L 283 280 196.00 - 364.00 Mn-54 Bq/L 314 331 231.70 - 430.30 Sr-90 Bq/L 0.093 no range given (1)

Zn-65 Bq/L 509 496 347.20 - 644.80 MaS13 Soil Cs-1 34 Bq/L 655 759 531.30 - 986.70 Cs-137 Bq/L 310 315 220.50 - 409.50 Co-57 Bq/L 234 242 169.40- 314.60 Co-60 Bq/L 219 212 148.40 - 275.60 Mn-54 Bq/L 512 485 339.50 - 630.50 K-40 Bq/L 642 604 422.80 - 785.20 Zn-65 Bq/L 890 810 567.00 - 1053 GrW13 Water Gr-A Bq/L 0.601 0.525 >0.0 - 1.05 Gr-B Bq/L 1.54 1.67 0.84 - 2.51 RdF13 AP Cs-1 34 Bq/sample 3.26 3.51 2.46 - 4.56 Cs-1 37 Bq/sample 2.05 2.26 1.58 - 2.94 Co-57 Bq/sample 4.78 4.92 3.44 - 6.40 Co-60 Bq/sample 3.02 3.03 2.12-3.94 Mn-54 Bq/sample 3.31 3.33 2.33 - 4.33 Sr-90 Bq/sample 1.15 1.35 0.95- 1.76 Zn-65 Bq/sample 3.14 3.14 2.20 - 4.08 GrF13 AP Gr-A Bq/sample 0.0764 0.232 >0.0 - 0.46 Gr-B Bq/sample 0.305 0.297 0.15 - 0.45 April 2005 RdV1 3 Vegetation Cs-134 Bq/kg 5.45 5 3.50 - 6.50 A Cs-1 37 Bq/kg 4.80 4.1 2.88 - 5.34 A Co-57 Bq/kg 13.4 9.88 6.92 - 12.84 A*

Co-60 Bq/kg 3.67 3.15 2.21 - 4.10 A Mn-54 Bq/kg 6.45 5.18 3.63 - 6.73 A Sr-90 Bq/kg 1.49 1.65 1.16 - 2.15 A Zn-65 Bq/kg 7.71 6.29 4.40 - 8.18 A October 2005 05-MaW14 Water Cs-134 Bq/L 142 167 116.90 - 217.10 A Cs-1 37 Bq/L 302 333 233.10 - 432.90 A Co-57 Bq/L 251 272 190.40 - 353.60 A Co-60 Bq/L 243 261 182.70 - 339.30 A H-3 Bq/L 547 527 368.90 - 685.10 A Mn-54 Bq/L 383 418 292.60 - 543.40 A Sr-90 Bq/L 8.75 8.98 6.29 - 11.67 A Zn-65 Bq/L 324 330 231.00 - 429.00 A D-5 117 of 206

TABLE D-3 DOE'S MIXED ANALYTE PERFORMANCE EVALUATION PROGRAM (MAPEP)

TELEDYNE BROWN ENGINEERING, 2005 (PAGE 2 OF 2)

Identification Reported Known Acceptance Month/Year Number Media Nuclide Units Value (a) Value (b) Range Evaluation (c)

October 2005 MaS14 Soil Cs-1 34 Bq/L 494 568 397.60 - 738.40 A Cs-1 37 Bq/L 446 439 307.30 - 570.70 A Co-57 Bq/L 506 524 366.80 - 681.20 A Co-60 Bq/L 289 287 200.90 - 373.10 A Mn-54 Bq/L 460 439 307.30 - 570.70 A K-40 Bq/L 626 604 422.80 - 785.20 A Zn-65 Bq/L 889 823 576.10- 1070 A GrW14 Water Gr-A Bq/L 0.858 0.79 0.21 - 1.38 A Gr-B Bq/L 1.22 1.35 0.85 - 1.92 A October 2005 RdF14 AP Cs-1 34 Bq/sample 4.11 3.85 2.70 - 5.01 A Cs-137 Bq/sample 3.16 3.23 2.26 -4.20 A Co-57 Bq/sample 6.14 6.2 4.34 - 8.06 A Co-60 Bq/sample 2.86 2.85 2.00 - 3.71 A Mn-54 Bq/sample 4.54 4.37 3.06 - 5.68 A Sr-90 Bq/sample 2.12 2.25 1.58 - 2.93 A Zn-65 Bq/sample 4.28 4.33 3.03 - 5.63 A GrF14 AP Gr-A Bq/sample 0.304 0.482 >0.0 - 0.80 A Gr-B Bq/sample 0.858 0.827 0.55 - 1.22 A RdV1 3 Vegetation Cs-134 Bq/kg 4.35 4.09 2.86 - 5.32 A Cs-1 37 Bq/kg 5.99 5.4 3.80 - 7.06 A Co-57 Bq/kg 17.0 13.30 9.31 - 17.29 W Co-60 Bq/kg 4.87 4.43 3.10-5.76 A Mn-54 Bq/kg 7.40 6.57 4.60 - 8.54 A Sr-90 Bq/kg 2.03 2.42 1.69 - 3.15 A Zn-65 Bq/kg 11.8 10.2 7.14 - 13.26 A

MAPEP reported the result as acceptable although the reported value of 13.4 is higher than the acceptance range upper limit of 12.84. The acceptance range was expanded to +- 4001%bias due to confusion regarding preparation process MAPEP did not corrected the acceptance range on the report.

(1) The Sr-90 in water was a MAPEP false positive test The TBE reported result of 0.093 + 0.0908 Bq/L was the forced Sr-90 activity and uncertainty, as required by MAPEP. The MDC for the sample was 0.145 pCi/L.

(a) Teledyne Brown Engineering reported result.

(b) The MAPEP known value is equal to 100% of the parameter present in the standard as determined by gravimetric and/or volumetric measurements made during standard preparation.

(c) DOE/MAPEP evaluation: A=acceptable, W=acceptable with waming, N=not acceptable.

D-6 118 of 206

TABLE D-4 ERAga) STATISTICAL

SUMMARY

PROFICIENCY TESTING PROGRAM ENVIRONMENTAL, INC., 2005 (Page 1 of 2)

Concentration (pCi/L)

Lab Code Date Analysis Laboratory ERA Control Resulto Result' Limits Acceptance STW-1051 02/15/05 Sr-89 28.0 +/- 1.2 29.4 20.7 - 38.1 Pass STW-1051 02/15/05 Sr-90 25.1 +/-0.7 24.4 15.7 - 33.1 Pass STW-1052 02/15/05 Ba-133 52.9 +/- 2.8 53.4 44.2 - 62.6 Pass STW-1052 02/15/05 Co-60 54.4 +/- 0.4 56.6 47.9 - 65.3 Pass STW-1052 02/15/05 Cs-134 67.7 +/- 1.8 64.9 56.2 - 73.6 Pass STW-1052 02/15/05 Cs-137 39.6 +/- 1.8 40.2 31.5 -48.9 Pass STW-1052 02/15/05 Zn-65 159.7 +/- 3.0 161.0 133.0 - 189.0 Pass STW-1053 02/15/05 Gr. Alpha 55.1 +/- 1.8 67.9 38.5 - 97.3 Pass STW-1053 02/15/05 Gr. Beta 46.8 +/- 1.3 51.1 38.5 - 97.3 Pass STW-1054 02/15/05 Ra-226 13.7 +/- 1.5 14.1 10.4 - 17.8 Pass STW-1054 02/15/05 Ra-228 13.3 +/- 0.6 13.7 7.8 - 19.6 Pass STW-1054 02/15/05 Uranium 5.1 +/-0.2 5.0 0.0 - 10.2 Pass STW-1055 05/17/05 Sr-89 45.1 +/-4.1 41.3 32.6 - 50.0 Pass STW-1055 05/17/05 Sr-90 7.5 +/- 0.9 5.9 0.0 - 14.6 Pass STW-1056 05/17/05 Ba-133 87.1 +/-2.0 88.4 73.1 - 104.0 Pass STW-1056 05/17/05 Co-60 38.4 +/- 0.8 37.0 28.3 - 45.7 Pass STW-1056 05/17/05 Cs-134 75.3 +/- 0.7 78.6 69.9 - 87.3 Pass STW-1056 05/17/05 Cs-137 201.0 +/- 8.4 194.0 184.0 - 218.0 Pass STW-1056 05/17/05 Zn-65 130.0 +/- 6.7 118.0 97.6 - 138.0 Pass STW-1057 05/17/05 Gr. Alpha 42.7 +/- 2.9 37.0 21.0 - 53.0 Pass STW-1057 05/17/05 Gr. Beta 34.0 +/- 0.4 34.2 25.5 - 42.9 Pass STW-1058 05/17/05 1-131 14.7 +/- 0.5 15.5 10.3 - 20.7 Pass STW-1059 05/17/05 Ra-226 6.6 +/- 0.1 7.6 5.6 -.9.5 Pass STW-1059 05/17/05 Ra-228 19.3 +/- 0.7 18.9 10.7 - 27.1 Pass STW-1059 05/17/05 Uranium 9.6 +/-0.1 10.1 4.9 - 15.3 Pass STW-1060 05/17/05 H-3 24100.0 +/- 109.0 24400.0 20200.0 - 28600.0 Pass STW-1067 08/16/05 Sr-89 29.1 +/-3.0 28.0 19.3 - 36.7 Pass STW-1067 08/16/05 Sr-90 36.0 +/- 0.6 33.8 25.1 - 42.5 Pass STW-1068 08/16/05 Ba-133 107.0 +/- 1.7 106.0 87.7 - 124.0 Pass STW-1068 08/16/05 Co-60 15.2 +/- 0.2 13.5 4.8 - 22.2 Pass STW-1068 08/16/05 Cs-134 89.1 +/-0.3 92.1 83.4 - 101.0 Pass STW-1068 08/16/05 Cs-137 72.1 +/- 1.0 72.7 64.0 - 81.4 Pass STW-1068 08/16/05 Zn-65 67.4 +/- 1.4 65.7 54.3 - 77.1 Pass STW-1069 08/16/05 Gr. Alpha 44.3 +/- 1.5 55.7 31.6 - 79.8 Pass STW-1069 08/16/05 Gr. Beta 58.4 +/- 2.1 61.3 44.0 - 78.6 Pass STW-1070 08/16/05 Ra-226 16.6 +/- 1.5 16.6 12.3 - 20.9 Pass STW-1070 08/16/05 Ra-228 6.2 +/- 0.3 6.2 3.5 - 8.9 Pass STW-1070 08/16/05 Uranium 4.5 +/- 0.1 4.5 0.0 - 9.7 Pass D-7 119 of 206

TABLE D-4 ERA!a) STATISTICAL

SUMMARY

PROFICIENCY TESTING PROGRAM ENVIRONMENTAL, INC., 2005 (Page 2 of 2)

Concentration (pCi/L)

Lab Code Date Analysis Laboratory ERA Control Result' Result' Limits Acceptance STW-1072 11/15/05 Sr-89 20.6 +/- 0.4 19.0 10.3 - 27.7 Pass STW-1072 11/15/05 Sr-90 15.0 +/- 0.3 16.0 7.3 -24.7 Pass STW-1073 11/15/05 Ba-133 31.8 +/- 1.8 31.2 22.5 - 39.9 Pass STW-1073 11/15/05 Co-60 85.0 +/- 1.4 84.1 75.4 - 92.8 Pass STW-1073 11/15/05 Cs-134 37.2 +/-2.1 33.9 25.2 -42.6 Pass STW-1073 11/15/05 Cs-137 27.8 +/-0.7 28.3 19.6 -37.0 Pass STW-1073 11/15/05 Zn-65 109.0 +/- 1.0 105.0 86.8 - 123.0 Pass STW-1074 a 11/15/05 Gr. Alpha 41.1 +/- 1.2 23.3 13.2 -33.4 Fail STW-1074 11/15/05 Gr. Beta 42.7 +/-0.5 39.1 30.4 -47.8 Pass STW-1075 11/15/05 1-131 20.5 +/- 0.6 17.4 12.2 - 22.6 Pass STW-1076 11/15/05 Ra-226 7.8 +/- 0.6 8.3 6.2 - 10.5 Pass STW-1076 e 11/15/05 Ra-228 5.5 +/- 0.6 3.5 2.0 - 5.0 Fail STW-1076 11/15/05 Uranium 15.5 +/- 0.3 16.1 10.9 - 21.3 Pass STW-1077 11/15/05 H-3 12500.0 +/-238.0 12200.0 10100.0 - 14300.0 Pass a Results obtained by Environmental, Inc., Midwest Laboratory as a participant in the crosscheck program for proficiency testing in drinking water conducted by Environmental Resources Associates (ERA).

b Unless otherwise indicated, the laboratory result is given as the mean +/- standard deviation for three determinations.

c Results are presented as the known values, expected laboratory precision (1 sigma, 1 determination) and control limits as provided by ERA.

d The original samples were calculated using an Am-241 efficiency. The samples were spiked with Th-232. Samples were recounted and calculated using the Th-232 efficiency. Results of the recount: 27.01 +/- 2.35 pCiUL.

Decay of short-lived radium daughters contributed to a higher counting rate. Delay of counting for 100 minutes provided better results.

The reported result was the average of the first cycle of 100 minutes, the average of the second cycle counts was 4.01 pCi/L D-8 120 of 206

TABLE D-5 DOE'S MIXED ANALYTE PERFORMANCE EVALUATION PROGRAM (MAPEPT ENVIRONMENTAL, INC., 2005 (Page 1 of 3)

Concentration b Known Control Lab Code' Date Analysis Laboratory result Activity Limits a Acceptance STW-1045 01/01/05 Gr. Alpha 0.45 +/- 0.10 0.53 0.00 - 1.05 Pass STW-1045 01/01/05 Gr. Beta 1.90 +/- 0.10 1.67 0.84 - 2.51 Pass STW-1046 01/01/05 Am-241 1.62 +/- 0.12 1.72 1.20 -2.24 Pass STW-1046 01/01/05 Co-57 239.40 +/- 1.20 227.00 158.90 -295.10 Pass STW-1046 01/01/05 Co-60 248.70 +/- 1.00 251.00 175.70 -326.30 Pass STW-1046 01/01/05 Cs-1 34 115.50 +/- 1.80 127.00 88.90 -165.10 Pass STW-1046 01/01/05 Cs-1 37 328.50 +/- 1.70 332.00 232.40 -431.60 Pass STW-1046 01/01/05 Fe-55 64.90 +/- 7.00 75.90 53.13 -98.67 Pass STW-1046 01/01/05 H-3 304.00 +/- 9.70 280.00 196.00 -364.00 Pass STW-1046 01/01/05 Mn-54 334.80 +/- 1.90 331.00 231.70 -430.30 Pass STW-1046 01/01/05 Ni-63 7.10 +/- 1.60 9.00 0.00 - 20.00 Pass STW-1046 01/01/05 Pu-238 0.01 +/- 0.02 0.02 0.00 - 1.00 Pass STW-1046 01/01/05 Pu-239/40 2.50 +/- 0.14 2.40 1.68 -3.12 Pass STW-1046 01/01/05 Sr-90 0.70 +/- 0.80 0.00 0.00 -5.00 Pass STW-1046 01/01/05 Tc-99 43.20 +/- 1.40 42.90 30.03 - 55.77 Pass STW-1046 01/01/05 U-233/4 3.31 +/- 0.20 3.24 2.27 - 4.21 Pass STW-1046 01/01/05 U-238 3.38 +/- 0.20 3.33 2.33 -4.33 Pass STW-1046 01/01/05 Zn-65 538.40 +/- 3.80 496.00 347.20 - 644.80 Pass STVE-1047 01/01/05 Co-57 10.60 +/- 0.20 9.88 6.92 - 12.84 Pass STVE-1047 01/01/05 Co-60 3.00 +/- 0.20 3.15 2.21 -4.10 Pass STVE-1047 01/01/05 Cs-134 4.80 +/- 0.40 5.00 3.50 - 6.50 Pass STVE-1047 01/01/05 Cs-137 4.10 +/- 0.30 4.11 2.88 - 5.34 Pass STVE-1047 01/01/05 Mn-54 5.10 +/- 0.30 5.18 3.63 - 6.73 Pass STVE-1047 01/01/05 Zn-65 6.20 +/- 0.50 6.29 4.40 -8.18 Pass STSO-1048 01/01/05 Am-241 96.60 +/- 10.00 109.00 76.30 - 141.70 Pass STSO-1048 01/01/05 Co-57 264.00 +/- 2.00 242.00 169.40 -314.60 Pass STSO-1048 01/01/05 Co-60 226.50 +/- 2.20 212.00 148.40 - 275.60 Pass STSO-1048 01/01/05 Cs-1 34 760.60 +/- 3.70 759.00 531.30 -986.70 Pass STSO-1048 01/01/05 Cs-137 336.20 +/- 3.60 315.00 220.50 - 409.50 Pass STSO-1048 01/01/05 K-40 663.70 +/- 18.00 604.00 422.80 - 785.20 Pass STSO-1048 01/01/05 Mn-54 541.30 +/- 3.90 485.00 339.50 - 630.50 Pass STSO-1048 01/01/05 Ni-63 924.30 +/- 17.20 1220.00 854.00 - 1586.00 Pass STSO-1048 01/01/05 Pu-238 0.60 +/- 0.80 0.48 0.00 - 1.00 Pass STSO-1048 01/01/05 Pu-239/40 78.00 +/- 4.80 89.50 62.65 -116.35 Pass STSO-1048 01/01/05 Sr-90 514.60 +/- 18.70 640.00 448.00 - 832.00 Pass STSO-1048 01/01/05 U-233/4 47.90 +/- 4.00 62.50 43.75 -81.25 Pass STSO-1048 01/01/05 U-238 226.30 +/- 8.60 249.00 174.30 - 323.70 Pass STSO-1048 01/01/05 Zn-65 851.30 +/- 7.30 810.00 567.00 - 1053.00 Pass STAP-1050 01/01/05 Gr. Alpha 0.11 +/- 0.03 0.23 0.00 - 0.46 Pass STAP-1050 01/01/05 Gr. Beta 0.38 +/- 0.05 0.30 0.15 -0.45 Pass D-9 121 of 206

TABLE D-5 DOE'S MIXED ANALYTE PERFORMANCE EVALUATION PROGRAM (MAPEPf ENVIRONMENTAL, INC., 2005 (Page 2 of 3)

Concentration b Known Control Lab Code' Date Analysis Laboratory result Activity Limits " Acceptance STAP-1049 01/01/05 Am-241 0.10 +/- 0.04 0.10 0.07 - 0.13 Pass STAP-1049 01/01/05 Co-57 4.76 +/- 0.64 4.92 3.44 - 6.40 Pass STAP-1049 01/01/05 Co-60 2.84 +/- 0.22 3.03 2.12 - 3.94 Pass STAP-1049 01/01/05 Cs-134 3.54 +/- 0.37 3.51 2.46 - 4.56 Pass STAP-1049 01/01/05 Cs-137 2.20 +/- 0.27 2.26 1.58 - 2.94 Pass STAP-1049 01/01/05 Mn-54 3.15 +/- 0.21 3.33 2.33 - 4.33 Pass STAP-1049 01/01/05 Pu-238 0.16 +/- 0.04 0.20 0.14 - 0.25 Pass STAP-1049 01/01/05 Pu-239/40 0.17 +/- 0.02 0.17 0.14 - 0.25 Pass STAP-1 049 e 01/01/05 Sr-90 2.24 +/- 0.34 1.35 0.95 - 1.76 Fail STAP-1049 01/01/05 U-233/4 0.34 +/- 0.02 0.34 0.24 - 0.44 Pass STAP-1049 01/01/05 U-238 0.35 +/- 0.02 0.35 0.25 - 0.46 Pass STAP-1049 01/01/05 Zn-65 3.12 +/- 0.15 3.14 2.20 - 4.08 Pass STW-1061 07/01/05 Am-241 2.21 +/- 0.13 2.23 1.56 - 2.90 Pass STW-1061 07/01/05 Co-57 293.20 +/- 7.30 272.00 190.40 - 353.60 Pass STW-1061 07/01/05 Co-60 275.70 +/- 1.30 261.00 182.70 - 339.30 Pass STW-1061 07/01/05 Cs-1 34 171.80 +/- 4.00 167.00 116.90 - 217.10 Pass STW-1061 07/01/05 Cs-137 342.10 +/- 2.20 333.00 233.10 - 432.90 Pass STW-1061 07/01/05 Fe-55 167.80 +/- 9.30 196.00 137.20 - 254.80 Pass STW-1061 07/01/05 H-3 514.20 +/- 12.60 527.00 368.90 - 685.10 Pass STW-1061 07/01/05 Mn-54 437.00 +/- 2.50 418.00 292.60 - 543.40 Pass STW-1061 07/01/05 Ni-63 105.10 +/- 3.60 100.00 70.00 - 130.00 Pass STW-1061 07/01/05 Pu-238 1.64 +/- 0.12 1.91 1.34 - 2.48 Pass STW-1061 07/01/05 Pu-239/40 2.32 +/- 0.13 2.75 1.93 - 3.58 Pass STW-1061 07/01/05 Sr-90 9.20 +/- 1.30 8.98 6.29 - 11.67 Pass STW-1061 07/01/05 Tc-99 72.30 +/- 2.30 66.50 46.55 - 86.45 Pass STW-1061 07/01/05 U-233/4 4.11 +/- 0.18 4.10 2.87 - 5.33 Pass STW-1061 07/01/05 U-238 4.14 +/- 0.18 4.26 2.98 - 5.54 Pass STW-1061 07/01/05 Zn-65 364.60 +/- 4.90 330.00 231.00 - 429.00 Pass STW-1062 07/01/05 Gr. Alpha 0.57 +/- 0.05 0.79 0.21 - 1.38 Pass STW-1062 07/01/05 Gr. Beta 1.36 +/- 0.05 1.35 0.85 - 1.92 Pass STSO-1063 t 07/01/05 Am-241 48.40 +/- 3.90 81.10 56.77 - 105.43 Fail STSO-1063 07/01/05 Co-57 608.30 +/- 2.80 524.00 366.80 - 681.20 Pass STSO-1063 07/01/05 Co-60 322.70 +/- 2.40 287.00 200.90 - 373.10 Pass STSO-1063 07/01/05 Cs-134 632.10 +/- 5.20 568.00 397.60 - 738.40 Pass STSO-1063 07/01/05 Cs-137 512.40 +/- 4.20 439.00 307.30 - 570.70 Pass STSO-1063 07/01/05 K-40 720.50 +/- 19.00 604.00 422.80 - 785.20 Pass STSO-1063 07/01/05 Mn-54 516.80 +/- 5.10 439.00 307.30 - 570.70 Pass STSO-1063 07/01/05 Ni-63 366.50 +/- 13.30 445.00 311.50 - 578.50 Pass STSO-1063 07/01/05 Pu-238 68.80 +/- 15.00 60.80 42.56 - 79.04 Pass STSO-1063 07/01/05 Pu-239/40 0.00 +/- 0.00 0.00 0.00 - 0.00 STSO-1063 07/01/05 Sr-90 602.90 +/- 17.20 757.00 529.90 - 984.10 Pass STSO-1063 07/01/05 U-233/4 61.50 +/- 1.00 52.50 36.75 - 68.25 Pass STSO-1063 07/01/05 U-238 164.50 +/- 16.70 168.00 117.60 - 218.40 Pass STSO-1063 07/01/05 Zn-65 874.70 +/- 8.40 823.00 576.10 - 1070.00 Pass D-10 122 of 206

TABLE D-5 DOE'S MIXED ANALYTE PERFORMANCE EVALUATION PROGRAM (MAPEPf ENVIRONMENTAL, INC., 2005 (Page 3 of 3)

Concentration b Known Control Lab Code' Date Analysis Laboratory result Activity Limits d Acceptance STVE-1064 07/01/05 Am-241 0.18 i 0.03 0.23 0.16 - 0.30 Pass STVE-1064 07/01/05 Co-57 15.90 i 0.20 13.30 9.31 - 17.29 Pass STVE-1 064 07/01/05 Co-60 4.80 i0.10 4.43 3.10 - 5.76 Pass STVE-1064 07/01/05 Cs-1 34 4.60 i 0.20 4.09 2.86 - 5.32 Pass STVE-1 064 07/01/05 Cs-1 37 5.90 i 0.30 5.43 3.80 - 7.06 Pass STVE-1064 07/01/05 Mn-54 7.20 i 0.20 6.57 4.60 - 8.54 Pass STVE-1064 07/01/05 Pu-238 0.04 i 0.02 0.00 0.00 - 1.00 Pass STVE-1064 07/01/05 Pu-239/40 0.13 i 0.02 0.16 0.11 - 0.21 Pass STVE-1064 07/01/05 Sr-90 2.80 i 0.30 2.42 1.69 - 3.15 Pass STVE-1064 07/01/05 U-233/4 0.28 +/- 0.03 0.33 0.23 - 0.43 Pass STVE-1064 07/01/05 U-238 0.33 +/- 0.04 0.35 0.24 - 0.45 Pass STVE-1064 07/01/05 Zn-65 11.00 +/- 0.50 10.20 7.14 - 13.26 Pass STAP-1065 07/01/05 Gr. Alpha 0.30 i 0.04 0.48 0.00 - 0.80 Pass STAP-1065 07/01/05 Gr. Beta 0.97 +/- 0.06 0.83 0.55 - 1.22 Pass STAP-1066 07/01/05 Am-241 0.14 +/- 0.03 0.16 0.11 -0.21 Pass STAP-1066 07/01/05 Co-57 5.81 +/- 0.17 6.20 4.34 - 8.06 Pass STAP-1066 07/01/05 Co-60 2.79 +/- 0.14 2.85 2.00 - 3.71 Pass STAP-1066 07/01/05 Cs-134 3.67 +/- 0.12 3.85 2.70 - 5.01 Pass STAP-1066 07/01/05 Cs-1 37 2.93 +/- 0.23 3.23 2.26 - 4.20 Pass STAP-1066 07/01/05 Mn-54 4.11 +/- 0.26 4.37 3.06 - 5.68 Pass STAP-1066 07/01/05 Pu-238 0.11 +/-0.02 0.10 0.07 - 0.13 Pass STAP-1066 07/01/05 Pu-239/40 0.10 +/- 0.01 0.09 0.06 - 0.12 Pass STAP-1066 07/01/05 Sr-90 2.25 i 0.29 2.25 1.58 - 2.93 Pass STAP-1066 07/01/05 U-233/4 0.28 +/- 0.02 0.27 0.19 - 0.35 Pass STAP-1066 07/01/05 U-238 0.28 +/- 0.02 0.28 0.20 - 0.37 Pass STAP- 1066 07/01/05 Zn-65 4.11 +/-0.26 4.33 3.06 - 5.68 Pass

Results obtained by Environmental, Inc., Midwest Laboratory as a participant In the Department of Energy's Mixed Analyte Performance Evaluation Program, Idaho Operations office, Idaho Falls, Idaho b Results are reported in units of Bq/kg (soil), Bq/L (water) or Bq/total sample (filters, vegetation) as requested by the Department of Energy.

Laboratory codes as follows: STW (water), STAP (air filter), STSO (soil), STVE (vegetation).

d MAPEP results are presented as the known values and expected laboratory precision (1sigma, 1 determination) and control limits as defined by the MAPEP.

The strontium carbonate precipitates were redissolved and processed. The average of the three analyses was 1.34 pCi/L, although the recovery was only 30%. The result of a new analysis was 1.56 pCVL.

f Incorrect sample weight used in calculation. Result of recalculation: 97.0 i 7.8 Bq/kg.

D-11 123 of 206

APPENDIX E ERRATA DATA 124 of 206

Table 5.0-4 RADIOLOGICAL ENVIRONMENTAL MONIIORING PROGRAM QUARTERLY

SUMMARY

Name of Faciliy Ouad Cities Nuclear Power Station Docket No. 50-254. 50-265 Location of Facility Rock Island. Illinois Reporting Period 2nd Ouaner 2004 (County, State)

Sample Type and Indicator Location with Highest Highest Control Number of Type Number of Locations Quarterly Mean_ Meana Locations Non-routine (Units) Analyses LLD Means Range Meana Results Range Range Air Gross 65 0.01 0.018 (52V52) Q-07, Clinton, 0.019 (12113) 0.019 (V123) 0 Particulates Beta (0.010-0.026) 8.9 mi NE, Sector C (0.012-0.024) (0.012-0.024) 3 (pCilnm)

Gamma Spec. 5 Cs-134 0.01 <LLD <LLD 0 Cd-137 0.01 <LLD . <LLD

< 0 Other Gammas 0.01-0.04 <LLD . . LLD 0 Airborne 1-131 30 0.07 <LLD . None 0 Iodine 3

(pCi/m )

Milk 1-131 5 1 <LLD . None 0 (PCi1L)

Gamma Spec. 5 Cs-134 15 <LLD . . None 0 Cs-137 18 <LID . None 0 Ba-140 60 <LLD None 0 La-140 15 <LLD . . None 0 Other Gammas 10-15 <LLD None 0 Fish Gamma Spec. 4 (pCi/g wet)

Cs-134 0.13 <LLD O<LD 0 Cs-137 0.15 <LLD , <LLD 0 Other ODCM-Required 0.13-0.26 <LLD . . <LLD 0 Gammas Other Gammas 0.20-0.30 <LLD . . <LLD 0 Bottom Gamma Spec. I Sediments (pCi/gd ry) Cs-134 0.15 <LLD . . None 0 Cs-137 0.18 <LLD . . None 0 a Mean and range based on detectable measurements only. Fractions indicated in parentheses.

Page 31 of 159 125 of 206

Table 5.0-5 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM QUARTERLY

SUMMARY

Name of Facilit Ouad Cities Nuclear Power Station Docket No. 50-254.50-265 Location of Facility Rock Island. Dlinois Reporting Period 3rd Ouarter 2004 (County, State)

Sample Type and Indicator Location with Highest Control Number of Type Number of Locations Highest Meana Locations Non-routine (Units) Analyses LLD Meana Quarterly Mean Range Meana Results Range Range Air Gross Beta 64 0.01 0.023 (51/51) Q-03, Onsite No. 3 0.025 (12/12) 0.024 (13/13) 0 Particulates (0.013-0.052) 0.6 mi S, Sector 1 (0.016-0.052) (0.016-0.031)

(pCi/m3 ) Gamma Spec. 5 Cs-134 0.01 <LLD 0 Cs-137 0.01 <LLD 0 Other Gammas 0.01-0.04 <LLD 0 Airborne -131 35 0.07 <LLD - - None 0 Iodine (pCi/m3)

Milk 1-131 7 1 <LLD - - None 0 (pCi/L)

Ganma Spec. 7 Cs-134 15 <LLD - - None 0 Cs-137 18 <LLD - - None 0 Ba-140 60 <LLD - - None 0 La-140 15 <LLD - - None 0 Other Gammas 10-15 Vegetation 1-131 18 0.06 <LLD - - <LLD 0 (pCigr. wet)

Ganma Spec. 18 Cs-I 34 0.06 <LLD - - <LLD 0 Cs-137 0.08 <LLD - <LLD 0 Other Gammas 0.01-0.10 <LLD - <LLD 0 Surface Gross Beta 6 4 4.4 (1/3) Q-33 Cordova 4.4 (1/3) 4.1 (1/3) 0 Water 3.3 mi. SSW, Sector K (pCi/L) Ganma Spec. 6 Cs-134 15 <LLD <LUD 0 Cs-137 18 <LLD <LLD 0 Other ODCM-Required 15-30 <LLD <LLD 0 Gammas idtiumn 2 200 <LUD <LLD 0 a Mean and range based on detectable measurements only. Fractions indicated in parentheses.

Page 33 of 159 126 of 206

Table 5.0-5 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM QUARTERLY

SUMMARY

Name of Facilit Ouad Cities Nuclear Power Stadon Docket No. 50-25450-265 Location of Facility Rock Island. lHinois Reporting Period 3rd Ouarter 2003 (Countyv State)

Sample Type and Indicator Location with Highest Control Number of Type Number of Locations Highest Meana Locations Non-routine (Units) Analyses LLD Meana Quartaly Mean Range Meana Results Range Range Air rosa Beta 65 0.01 0.027 (52152) Q-07, Clinton 0.030(13/13) 0.030 (13/13) 0 Particulates (0.015-0.053) 8.9 mi NE, Sector C (0.017-0.050) (0.017-0.050)

(pCil3) Gamma Spec. 5 Cs-134 0.01 <LLD . 0 Cs-137 0.01 <LLD 0 Other Gammas 0.01-0.04 <LLD 0 Airborne -131 35 0.07 <LLD . None 0 Iodine Milk -131 6 1 <LLD . . None 0 (pCi/L)

Gamma Spec. 6 Cs-134 15 <LLD . None 0 Cs-137 18 LD . None 0 Ba -140 60 <LLD . . None 0 La-140 15 <LLD None 0 Other Gammas 10-15 Vegetation -131 14 0.06 <LLD <LLD 0 (pCi/gr. wet)

Gamma Spec. 14 Cs- 134 0.06 <LLD <LLD

< 0 Cs-137 0.08 <LID <LLD 0 Other Gammas 0.01-0.10 <LLD <LlD 0 Surface Gross Beta 6 4 4.5 (213) Q-33 Cordova 4.5 (213) <LLD 0 Water (4.3-4.7) 3.3 mi. SSW, Sector K (4.3-4.7)

(pCi/L) Gamma Spec. 6 Cs-134 15 <LID <LLD 0 Cs-137 I8 <LLD <LD 0 Other ODCM-Required 15-30 <LLD . <LLD 0 Gammas Tritdum 2 200 <LLD . <LLD 0 a Mean and range based on detectable measurements only. Fractions indicated In parentheses.

1-29 127 of 206

Table 5.0-5 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM QUARTERLY

SUMMARY

Name of Facility Ouad Cities Nuclear Power Station Docket No. 50-25450-265 Location of Facility Rock Island. Dlinois Reporting Pedod 3rd uarter 2002 (County, State)

Sample Type and Indicator Location with Highest Control Number of Type Number of Locations Highest Meana Locations Non-routine (Units) Analyses LLD Meana Quarterly Mean Range Meana Results Range Range Air Gross Beta 63 0.01 0.026 (50/50) Q-07, Clinton 0.028 (13/13) 0.028 (13/13) 0 Particulates (0.014-0.037) 8.9 mi NE, Sector C (0.019-0.037) (0.019-0.037)

(pCi/mi ) Gamma Spec. 5 Cs-134 0.01 <LID 0 Cs-137 0.01 <LLD 0 Other Gammas 0.01-0.04 <LLD 0 Ailborne 1-131 35 0.07 <LL None 0 Iodine 3

(pCi/mn ) __ _ _ _ _ _ _ _ _ _ __ _ _ _ __ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ __ _ _ _ _ _ _

Milk -131 6 0.5 <LLD . None 0 KU~iL)

Gamma Spec. 6 Cs- 134 15 <LU) None 0 Cs-137 18 <LLD - None 0 Ba/La-140 15 <LLD - None 0 Other Gammas 10-15 <LUD - None 0 Vegetation 1-131 10 0.06 <LLD - <LLD 0 (pCi/gr. wet)

Gamma Spec. 10 Cs-134 0.06 <LLD - <LLD 0 Cs-137 0.08 <LLD - <LID 0 Other Gammas 0.01-0.10 <LLD - <LLD 0 Surface Gross Beta 6 4 4.3 (2/3) Q-33 Cordova 4.3 (2/3) <LID 0 Water (4.3-4.3) 3.3 mi. SSW, Sector K (4.3-4.3)

(pCi/L) Gamma Spec. 6 Cs-134 15 <LID <LLD 0 Cs-137 18 <LID <LID 0 Other ODCM-Required 15-30 <LUD <LLD 0 Gammas

_dtium 2 200 <LLD <LLD 0 a --- --

MeanI WILI range oase on1 UULeV"MJ 111a-QrW -. uY. rlaaUons LM.LLcA II Pm paHUnee.

1-30 128 of 206

h Table 5.0-5 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM QUARTERLY

SUMMARY

Name of Facility Quad Cidies Nuclear Power Station Docket No. 50-254. 50-265 Location ofFaciliy Rock Island. Illinois Reporting Period 3rdOuarter 2001 (County, State)

Sample Type and Indicator Location with Highest Control Number of Type Number of Locations Highest Meana Locations Non-routine (Units) Analyses LLD Means Quarterly Mean Range Meana Results Range Range Air Grss Beta 65 0.01 0.026 (52152) Q-07, Clinton 0.028 (13/13) 0.028 (13/13) 0 Particulates (0.018-0.039) 8.9mi NE, Sector C (0.0204.038) (0.020-0.038)

(pCi/m3) Gamma Spec. 5 Cs-134 0.01 <LID . 0 Cs-137 0.01 <LLD 0 Other Gammas 0.01-0.04 <LLD O_0 Airborne -131 35 0.07 <LLD - - None 0 Iodine 3

(pCi/m )

Milk -131 6 0.5 <LLD . None 0 (pCi/L)

Gamma Spec. 6 Cs-134 15 <LD) - . None 0 Cs-137 18 <LLD . None 0 Ba/La-140 15 <LLD - None 0 Other Gammas 10-15 <Ln -. None 0 Vegetation -131 12 0.06 <LU) - - <LLD 0 (pCl/gr. wet)

Gamma Spec. 12 Cs-134 0.06 <LL - - <LD 0 Cs-137 0.08 <LLD - - <LLD 0 OtherGammas 0.014.10 <LLD - - <LLD 0 Surface Gross Beta 6 4 4.9(213) Q-33 Cordova 4.9(213) 4.6(213) 0 Water (4.6-5.1) 3.3 mi. SSW. Sector K (4.6-5.1) (4.3-4.9)

(pCU/L) Gamma Spec. 6 Cs-134 15 <LLD <LLD 0 Cs-137 18 <LLD <LLD 0 Other ODCM-Required 15-30 <LD <LLD 0 Gammas rtium 2 200 <LLD <LID 0 a Mean and range based on detectable measurements only. Fractions indicated in parentheses.

I-32 129 of 206

0 -

Table 5.0-6 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM QUARTERLY

SUMMARY

Name of Facility Ouad Cities Nuclear Power Station Docket No. 50-254.50-265 Location of Facilit Rock Island. Illinois Reporting Period 4th Quarter 2001 (Count, State)

Sample Type and Indicator Location with Highest Control Number of Type Number of Locations Highest Meana Locations Non-routine (Units) Analyses LLD Meana Quarterly Mean Range Meana Results Range Range Air Gross Beta 65 0.01 0.031 (52/52) Q-07, Clinton 0.035 (13/13) 0.035 (13/13) 0 Particulates (0.020-0.046) 8.9 mi NE, Sector C (0.024-0.048) (0.024-0.048)

(pCi/m3) Gamma Spec. 5 Cs-134 0.01 <LLD 0 Cs-137 0.01 <LLD 0 Other Gammas 0.01-0.04 <LD . 0 Airbome Iodine 1-131 30 0.07 4LD None 0 3

(pCi/mn) _ _ _ _ _ _ _ _ _ _ __ _ _ _ _ _ _

Milk 1-131 4 5 .0 10 .5 b <LLD None 0 (pCi/L)

Gamma Spec. 4 Cs-134 15 <LLD None 0 Cs-137 18 <LLD None 0 BalLa-140 1I5 n - -None 0 Ohter Gammas 10-15 <L - None 0 Fish Gamma Spec. 10 (pCi/g wet)

Cs-134 0.10 <LLD <LLD 0 Cs-137 0.10 <LLD . <LLD 0 Other ODCM-Required 0.1340.26 <LLD <LLD 0 Gammas

_ Other Gammas 0.20-.030 <LLD <LID 0 Bottom a Spec. I Sediments (pCi/g dry) Cs-134 0.15 <LLD <LLD 0 Cs-137 0.18 <LLD <LLD 0 Other ODCM-Required 0.10-0.60 <LLD <LUD 0 Gammas Surface Water Gross Beta 6 4 <LLD . < 0 (pCi/L)

Gamma Spec. 6 Cs- 134 10 <LLD d<LD 0 Cs-137 10 <LLD <LLD 0 Other ODCM- 15-30 <LLD <LLD 0 Required Gammas Tritium 2 200 <LLD <LLD 0 a Mean and range based on detectable measurements only. Fractions indicated in parentheses.

b November- April LLD=5.0; May - Octotober LLD=0.5.

1-34 130 of 206

APPENDIX F EFFLUENT DATA 131 of 206

TABLE OF CONTENTS INTRODUCTIO N .................................................................................................................... 1

SUMMARY

.............................................................................................................................2 1.0. EFFLUENTS.......................................................................................................3 1.1. Gaseous Effluents to the Atmosphere ............................................... 3 1.2. Liquids Released to Mississippi River ............................................... 3 2.0. SOLID RADIOACTIVE WASTE .............................................. 3 3.0. DOSE TO MAN ............................................... 4 3.1. Gaseous Effluent Pathways .............................................. 4 3.1.1. Noble Gases ............................................ 4 3.1.1.1. GammaDoseRates ............................................... 4 3.1.1.2. Beta Air and Skin Dose Rate ...................................... 4 3.1.2. Radioactive Iodine. .................................................................... 5 3.1.2.1. Dose to Thyroid ............................................... 5 3.2. Liquid Effluent Pathways .............................................. 6 3.3. Assessment of Dose to Member of Public .............................................. 6 4.0. SITE METEOROLOGY ............................................... 7 i

132 of 206

Table of Contents (cont.)

APPENDIX F-1 EFFLUENT TABLES.............................................................................. F-1.1 Station Releases Table 1.1-1 Gaseous Effluents - Summation of all Releases ....................... F-1.2 Table 1.2-1 Liquid Effluents - Summation of all Releases ............................ F-1.3 Table 2.0-1 Solid Radwaste Annual Report .............................................. F-1.4 Table 3.1-1 Maximum Doses Resulting from Airborne Releases ................. F-1.5 Table 3.2-1 Maximum Doses Resulting from Liquid Effluents ...................... F-1.6 Table 3.3-1 1OCRF20 Compliance Assessment .......................................... F-1.7 Table 3.4-1 Maximum Doses Resulting from Airborne Releases Based On Concurrent Meteorological Data .................................... F-1.8 ii 133 of 206

INTRODUCTION Units 1 and 2 of the Quad Cities Nuclear Power Station, located near Cordova, Illinois next to the Mississippi River, are 2957 MW boiling water reactors. The station has been designed to keep releases to the environment at levels below those specified in the regulations.

Liquid effluents from Quad Cities Nuclear Power Station are released to the Mississippi River in controlled batches after radioassay of each batch. Gaseous effluents are released to the atmosphere after delay to permit decay of short-lived (noble) gases. Releases to the atmosphere are calculated on the basis of analyses of grab samples of noble gases as well as continuously collected composite samples of iodine and particulate activity sampled during the course of the year. The results of effluent analyses are summarized on a monthly basis and reported to the Nuclear Regulatory Commission as required per Technical Specifications. Airborne concentrations of noble gases, 1-131, and particulate radioactivity in offsite areas are calculated using isotopic composition of effluent and meteorological data.

Environmental monitoring is conducted by sampling at indicator and control (background) locations in the vicinity of Quad Cities Nuclear Power Station to measure changes in radiation or radioactivity levels that may be attributable to station operations. If significant changes attributable to Quad Cities Nuclear Power Station are measured, these changes are correlated with effluent releases. External gamma radiation exposure from noble gases and internal dose from 1-131 in milk are the critical pathways at this site; however, an environmental monitoring program is conducted which also includes other pathways.

134 of 206

SUMMARY

Calculations based on gaseous and liquid effluents and hydrogen addition activities indicate that public does due to radioactive material attributable to Quad Cities Nuclear Power Station during the period does not exceed regulatory or Offsite Dose Calculation Manual (ODCM) limits.

The Total Effective Dose Equivalent (TEDE) due to licensed activities at Quad Cities Nuclear Power Station calculated for the maximally-exposed individual for the period is 6.73 mrem. The annual limit on TEDE is 100 mrem. Most of the dose (6.02 mrem) is due to direct radiation from Unit 1 and Unit 2 turbines. The remaining 0.71 mrem is due to the maximum calculated dose from radionuclides released from the station in gaseous and liquid effluents.

The assessment of radiation doses to the public is performed in accordance with the ODCM. The results of these analyses confirm that the station is operating in compliance with 10CFR50 Appendix I, 10CFR20 and 40CRF190.

2 135 of 206

1.0 EFFLUENTS 1.1 Gaseous Effluents to the Atmosphere Measured concentrations and isotopic composition of noble gases, radioiodine, and particulate radioactivity released to the atmosphere during the year, are listed in Table 1.1-1. A total of 1.83E+02 curies of fission and activation gases were released with a maximum quarterly release rate of 1.23E+01 pCi/sec, for both units.

A total of 5.23E-03 curies of 1-131 were released during the year with a maximum average quarterly release rate of 4.77E-04 pCi/sec.

A total of 1.14E-02 curies of beta-gamma emitters were released as airborne particulate matter with a maximum average release rate of 8.76E-04 pCi/sec. Alpha-emitting radionuclides were below the lower limit of detection (LLD) for the year.

A total of 1.86E+02 curies of tritium were released with a maximum average quarterly release rate of 7.38E+00 uCi/sec.

1.2 Liquids Reltased to the Mississippi River A total of 3.49E+06 liters of radioactive liquid wastes (prior to dilution) containing 9.44E-03 curies (excluding tritium, noble gases and alpha) were discharged from the station. These wastes were released at a maximum quarterly diluted average concentration of 1.73E-09 pCi/ml. A total of 4.74E-05 curies of alpha radioactivity was released in liquid waste. A total of 4.40E+01 curies of tritium was released at a maximum quarterly average diluted concentration of 4.31 E-06 pCi/ml. Quarterly release totals of principal radionuclides in liquid effluents are given in Table 1.2-1.

2.0 SOL ID RADIOACTIVE WASTE Thirty shipments of solid radioactive waste were shipped to waste processors via truck during 2005; sixty-five shipments were sent, via truck, to disposal sites (Table 2.0-1). For detail, refer to the Quad Cities Nuclear Power Station 2005 Annual Radiological Effluent Report.

3 136 of 206

3.0 DOSE TO MAN 3.1 Gaseous Effluent Pathways Table 3.1-1 summarizes the doses resulting from releases of airborne radioactivity via the different exposure pathways.

3.1.1 Noble Gases 3.1.1.1 Gamma Dose Rates Offsite Gamma air and whole body dose rates are shown in Table 3.1-1 and were calculated based on measured release rates, isotopic composition of the noble gases, and average meteorological data for the period. Dose rates based on concurrent meteorological data are shown in Table 3.4-1. Based on measured effluents and average meteorological data, the maximum total body dose to an individual would be 2.91 E-02 mrem for the year (Table 3.1-1), with an occupancy or shielding factor of 0.7 included. The maximum total body dose based on measured effluents and concurrent meteorological data would be 6.37E-02 mrem (Table 3.4-1). The maximum gamma air dose was 1.14E-03 mrad (Table 3.1-1) based on measured effluents and average meteorological data, and 7.79E-03 mrad based on concurrent meteorological data (Table 3.4-1).

3.1.1.2 Reta Air and Skin Dose Rates The range of beta particles in air is relatively small (on the order of a few meters or less);

consequently, plumes of gaseous effluents may be considered "infinite" for purpose of calculating the dose from beta radiation incident on the skin.

However, the actual dose to sensitive skin tissues is difficult to calculate due to the effect of the beta particle energies, thickness of inert skin and clothing covering sensitive tissues. For purposes of this report the skin is taken to have a thickness of 7.0 mg/cm 2 and an occupancy factor of 1.0 is used. The skin dose from beta and gamma 4

137 of 206

radiation for the year was 7.55E-02 mrem (Table 3.4-1)

The maximum offsite beta air dose for the year was 6.54E-04 mrad based on average meteorological data Table 3.1-1) and 1.20E-03 mrad based on concurrent meteorological data (Table 3.4-1).

Doses calculated using average meteorology and those calculated using concurrent meteorology differ for two reasons:

1. Concurrent meteorology results in different plume dispersion and deposition characteristics.

2. Concurrent wind direction will cause variations in the sector of dispersion and deposition. This variation results in varying distances used in calculating dispersion and deposition parameters.

3.1.2 Radioactive Iodine The human thyroid exhibits a significant capacity to concentrate ingested or inhaled iodine. The radioiodine, 1-131, released during routine operation of the station, may be made available to a person resulting in a dose to the thyroid. The principal pathway of interest for this radionuclide is ingestion of radioiodine in milk.

3.1.2.1 Dose to Thyroid The hypothetical thyroid dose to the maximum exposed individual living near the station via ingestion of milk was calculated. The radionuclide considered was 1-131 and the source of milk was taken to be the nearest dairy farm with the cows pastured from May through October. The maximum annual thyroid dose was 6.79E-01 mrem (Table 3.1-1[infant]).

5 138 of 206

3.2 Liquid Effluent Pathways The three principal pathways through the aquatic environment for potential doses to man from liquid waste are ingestion of potable water, eating aquatic foods, and exposure while on the shoreline.

Not all of these pathways are significant or applicable at a given time or station but a reasonable approximation of the dose can be made by adjusting the dose formula for season of the year or type and degree of use of the aquatic environment. NRC developed equations* were used to calculate the doses to the whole body, lower GI tracts, thyroid, bone and skin; specific parameters for use in the equations are given in the Offsite Dose Calculation Manual.

The maximum whole body dose for the year was 7.05E-05 mrem (adult). The maximum organ dose was 1.13E-04 mrem (Table 3.2-1 [teen liver]).

3.3 Assessment of Dose to Member of Public During the period January to December, 2005, Quad Cities Nuclear Power Station did not exceed the following limits as shown in Table 3.1-1 and Table 3.2-1 (based on yearly average meteorological data), and as shown in Table 3.4-1 (based on concurrent meteorological data):

The RETS limits on dose or dose commitment to a member of the public due to radioactive materials in liquid effluents from each reactor unit (3 mrem to the whole body or 10 mrem to any organ during any calendar quarter; 6 mrem to the whole body or 20 mrem to any organ during the calendar year).

The RETS limits on air dose in noble gases released in gaseous effluents to a member of the public from each reactor unit (5 mrads for gamma radiation or 10 mrad for beta radiation during any calendar quarter; 10 mrad for gamma radiation or 20 mrad for beta radiation during a calendar year).

The RETS limits on dose to a member of the public due to iodine-131, iodine-133, tritium, and radionuclides in particulate form 'with half-lives greater than eight days in gaseous effluents released from each reactor unit (7.5 mrem to any organ during any calendar quarter; 15 mrem to any organ during any calendar year).

6 139 of 206

The RETS 40CFR190 limits for dose due to radioactive liquid and gaseous effluents to the whole body or any organ (25 mrem during the calendar year) and to the thyroid (75 mrem during the calendar year).

The 10CFR20 limit on Total Effective Dose Equivalent to individual members of the public (100 mrem) during any calendar year.

4.0 SITE METEOROLOGY A summary of the site meteorological measurements taken during each calendar quarter of the year is given in Appendix E. The data are presented as cumulative joint frequency distributions of the wind direction for the 296' level and wind speed class by atmospheric stability class determined from the temperature difference between the 296' and 33' levels. Average data recovery for all measurements on the tower as 98.9% during 2005 (Table 3.4-1).

Nuclear Regulatory Commission, Regulatory Guide 1.109 (Rev. 1) 7 140 of 206

APPENDIX F-1 EFFLUENT TABLES F-1 .1 141 of 206

Table 1.1-1 Gaseous Effluents - Summation Of All Releases Effluent & Waste Disposable Summary Period: January - December 2005 Unit: 1 & 2 A. Fission & Activation Gases Unit Quarter 1 Quarter 2 Quarter Quarter Est. Total 3 4 Error %

I. Total Release Ci 9.55E+01 1.67E+01 2.99E+01 4.09E+01 12.5

2. Average release rate for the period pCi/sec 1.23E+01 2.13E+00 3.76E+00 5.14E+00

3. Percent of ODCM limitt11 %Y 1.40E-02 1.78E-03 2.88E-03 3.78E-03

% fi 4.12E-03 4.60E-04 6.93E-04 9.79E-04 B. Iodine

1. Total Iodine- 131. Ci 3.71E-03 8.45E-04 4.02E-04 2.77E-04 41.6jl

2. Average release rate for the period pCi/sec 4.77E-04 1.07E-04 5.06E-05 3.48E-05

3. Percent of ODCM limit % NA NA NA NA C. Particulates

1. Particulates with half-lives> 8 days l Ci 1.25E-03 6.89E-03 l 2.60E-03 6.55E-04 32.1

2. Average release rate for the period pCi/sec 1.61E-04 8.76E-04 3.27E-04 8.24E-05

3. Percent of ODCM limit % NA NA NA NA

4. Gross alpha radioactivity Ci <LLD <LLD <LLD <LLD D. Tritium I

1. Total Release Ci 5.74E+01 [3.54E+01 4.41E+01 4.88E+01 6.3

2. Averaae release rate for the veriod uCi/sec 7.38E+00 4.50E+00 I 5.55E+/-O00 I 6.15E+/-00

3. PercentofODCMlimit % NA [ NA ( NA NA E. Iodine 131 & 133, Tritium &

Particulate

1. Percent of ODCM limit % I 6.21E+00 I 1.65E+00 I 7.01E-01 I 4.89E-01 I (1) % Noble gas gamma/noble gas beta dose limits F-1.2 142 of 206

Table 1.2-1 Liquid Effluents - Summation Of All Releases Effluent & Waste Disposal Summary Period: January - December 2005 Unit: 1 & 2 A. Fission & Activation Products Unit Quarter Quarter Quarter Quarter Est. Total 1 2 3 4(2) Error %

I. Total Release (not including tritium, Ci 6.87E-03 7.73E-04 9.43E-04 8.5 1E-04 4.1 gases & alpha) 2 Average diluted concentration during p+/-Ci/mL 1.73E-09 1.14E- I0 1.17E-I 0 2.45E- 12 period

3. Percent of applicable limit WB7TI4.92E-02 3.72E-02 4.58E-03 5.77E-05 l O 2.58E-02 1.75E-02 5.5 1E-03 2.82E-05

4. Maximum diluted concentration during PCi/ML 2.99E-09 2.25E-10 1.23E-10 NAt2 )

batch discharges B. Tritium I. Total Release Ci 1.71E+01 1.83E+01 8.58E+00 <LLD 4.1

2. Average diluted concentration during pCi/mL 4.31 E-06 2.69E-06 1.06E-06 NA(2 )

period

3. Percent of applicable limit % 1.44E-01 9.OOE-02 3.53E-02 NA(2 )

C. Dissolved & Entrained Gases

1. Total Release Ci 1.82E-04 <LLD <LLD <LLD 4.1

2. Average diluted concentration during pCi/mL 4.60E-I I NA NA NA period

3. Percent of applicable limit 2.30E-05 NA NA NA D. Gross Alpha Activity

. Total Release l Ci 4.74E-05 <LLD LLD <LLD 14.8 E. Volume Of Waste Released (prior Liters 1.23E+06 11.23E+06 1.03E+06 O.OOE+00 to dilution) I F. Volume Of Dilution Water Used Liters 2.53E+1 I 3.64E+11 4.93E+11 3.48E+I 1 I During Period (1) Whole Body/Organ (ODCM)

(2) No batch discharges I F-1.3 143 of 206

Table 2.0-1 Solid Radwaste Annual Report Solid Waste and Irradiated Fuel Shipments A. Solid Waste Shipped Offsite for Burial or Disposal (Not irradiated fuel)

1. Types of Waste Types of Waste Total Quantity Total Period Est. Total (mi3 ) Activity (Ci) Error %

a. Spent resins, filter sludges, 1.54E+02 2.80E+03 2005 2.50E+01 evaporator bottoms, etc

b. Dry compressible waste, 1.89E+03 5.78E+01 2005 2.50E+01 contaminated equip, etc

c. Irradiated components, control 3.96E+01 1.8 1E+02 2005 2.50E+01 rods, etc

d. Other (describe) Combined 1.01E+02 7.64E+02 2005 2.50E+01 Packages of a. and b. II

2. Estimate of major nuclide composition (by waste type)

Major Nuclide Composition _

a. Mn-54 3.34E+00 Fe-55 6.79E+01 Co-60 2.67E+01

b. Mn-54 1.52E+00 Fe-55 5.95E+01 Co-60 2.84E+01 Zn-65 6.47E+00 Cs-137 3.26E+00

c. Mn-54 1.12E+00 Fe-55 6.63E+01 Co-60 2.98E+01 Ni-63 7.81E-01

3. Solid Waste Disposition Number of Shipments Mode of Transportation Destination 30 Highway Processor 65 Highway Disposal B. Irradiated Fuel Shipments (disposition)

Number of Shipments Mode of Transportation Destination 2 Highway Disposal C. Changes to the Process Control Program Submitted with this report is Revision 3 of RW-AA-100, Process Control Program for Radioactive Wastes. No significant process changes made. Changes are administrative in nature.

F-1.4 144 of 206

Table 3.1-1 Maximum Doses Resulting from Airborne Releases GASEOUS ANNUAL DOSE

SUMMARY

REPORT (Composite Critical Receptor - Limited Analysis)

Release ID ............ : 1 All Gas Releases Year .................. : 2005 Coefficient Type ...... : Historical Receptor .............. : 5 Composite Crit. Receptor - IP Distance (meters)..... : 0.0 Compass Point ......... : 0.0

MAXIMUM PERIOD DOSE TO LIMIT (I(ny Organ) ================================

Dose Age Dose Limit Admin Admin % T.Spec T.Spec %

Period Group Organ (mrem) Period Limit of Limit Limit of Limit Quarter__1-IFAN ------- Quarter 5 _63E+00 7 _50E+0 Quarter 1 INFANT THYROIE 4.66E-01 Quarter 5. 63E+00 8.28E+00 7. 50E+00 6.21E+00 Quarter 2 INFANT THYROIE 1.24E-01 Quarter 5. 63E+00 2. 20E+00 7. 50E+00 1. 65E+00 Quarter 3 INFANT THYROID 5.25E-02 Quarter 5. 63E+00 9. 34E-01 7.50E+00 7.01E-01 Quarter 4 INFANT THYROIE 3.67E-02 Quarter 5. 63E+00 6.53E-01 7.50E+00 4.90E-01 Annual INFANT THYROID 6.79E-01 Annual 1.13E+01 6.03E+00 1.50E+01 4.52E+00

MAXIMUM PERIOD DOSE TO LIMIT (Tot Body) ==========2=====================

Dose Age Dose Limit Admin Admin % T. Spec T.Spec %

Period Group Organ (mrem) Period Limit of Limit Limit of Limit Quarter__1-CHIL --B--D- 3 Quarter 5.______ 7 _ OE+00 Quarter 1 CHILD TBODY 3.48E-0 3 Quarter 5.25E+00 6. 63E-02 7. 50E+00 4. 64E-02 Quarter 2 CHILD TBODY 1. 60E-0 2 Quarter 5.25E+00 3.05E-01 7. 50E+00 2.14E-01 Quarter 3 CHILD TBODY 6.90E-0 3 Quarter 5.25E+00 1.31E-01 7. 50E+00 9.20E-02 Quarter 4 CHILD TBODY 2.70E-0 23 Quarter 5.25E+00 5. 14E-02 7.50E+00 3. 60E-02 Annual CHILD TBODY 2.91E-0)2 Annual 1.05E+01 2. 77E-01 1. 50E+01 1. 94E-01 GASEOUS ANNUAL DOSE

SUMMARY

REPORT (Composite Critical Receptor - Limited Analysis)

Release ID ............ : 1 All Gas Releases Year .................. : 2005 Coefficient Type ...... : Historical Receptor .............. : 4 Composite Crit. Receptor - NG Distance (meters)..... : 0.0 Compass Point ......... : 0.0

MAXIMUM PERIOD NG DOSE TO LIMIT (Gamma) ==============================

Dose Dose Limit Admin Admin % T.Spec T.Spec %

Period Dose Type (mrad) Period Limit of Limit Limit of Limit Quarter__1--Gamma- Quarter ________ --------

Quarter 1 Gamma 7.01E-04 Quarter 3.75E+00 1.87E-02 5.OOE+00 1.40E-02 Quarter 2 Gamma 8.99E-05 Quarter 3.75E+00 2.40E-03 5.OOE+00 1.80E-03 Quarter 3 Gamma 1.44E-04 Quarter 3.75E+00 3.84E-03 5. O0E+00 2. 88E-03 Quarter 4 Gamma 2.05E-04 Quarter 3.75E+00 5.47E-03 5. OOE+00 4.10E-03 Annual Gamma 1.14E-03 Annual 7.50E+00 1.52E-02 1.OOE+01 1.14E-02

MAXIMUM PERIOD NG DOSE3 TO LIMIT (Beta) ==============================

Dose Dose Limit Admin Admin % T.Spec T.Spec %

Period Dose Type (mrad) Period Limit of Limit Limit of Limit Quarter__1--Beta--

4.12E-04 Quarter 7.50E+00 5.49E-03 1.OOE+01 4.12E-03 Quarter 2 Beta 4.74E-05 Quarter 7.50E+00 6.31E-04 1. OOE+01 4.74E-04 Quarter 3 Beta 6.93E-05 Quarter 7.50E+00 9.24E-04 1.00E+01 6.93E-04 Quarter 4 Beta 1.25E-04 Quarter 7.50E+00 1. 67E-03 1. OOE+01 1.25E-03 Annual Beta 6.54E-04 Annual 1.50E+01 4. 36E-03 2.00E+01 3.27E-03 F-1.5 145 of 206

Table 3.2-1 Maximum Doses Resulting from Liquid Effluents LIQUID ANNUAL DOSE

SUMMARY

REPORT Release ID ............ : 1 All Liquid Releases Year ................ : 2005 Liquid Receptor ....... : 0 Liquid Receptor

== MAXIMUM PERIOD DOSE TO LIMIT (Any Organ) =======-== == = = -==== == ----------------- =

Dose Age Dose Limit Admin Admin % T.Spec T.Spec %

Period Group Organ (mrem) Period Limit of Limit Limit of Limit Quarter 1-TEE - --I--ER Quarter I TEEN LIVER 4.55E-05 Quarter 3.75E+00 1. 21E-03 5.00Ei-00 9. 09E-04 Quarter 2 TEEN LIVER 7.21E-05 Quarter 3.75E+00 1.92E-03 5.OOE+00 1. 44E-03 Quarter 3 TEEN LIVER 1.93E-05 Quarter 3.75E+00 5. 16E-04 5.OOE+00 3. 87E-04 Quarter 4 ADULT GILLI 1.40E-06 Quarter 3.75E+00 3. 73E-05 5.00E+00 2. 80E-05 Annual TEEN LIVER 1.13E-04 Annual 7.50E+00 1.51E-03 1.00E+01 1.13E-03

MAXIMUM PERIOD DOSE TO LIMIT (Tot Body) ========:=========================

Dose Age Dose Limit Admin Admin % T. Spec T.Spec %

Period Group Organ (mrem) Period Limit of Limit Limit of Limit Quarter 1-ADUL T--DDY- 5 Quarter -------- 1 _ E+00 Quarter 1 ADULT TBODY 2.61E-0 5 Quarter 1.13E+00 2.32E-03 1.50E+00 1.74E-03 Quarter 2 ADULT TBODY 4.64E-0 5 Quarter 1.13E+00 4.12E-03 1.50E+00 3.09E-03 Quarter 3 ADULT TBODY 1.26E-0 5 Quarter 1.13E+00 1. 12E-03 1. 50E+00 8. 41E-04 Quarter 4 ADULT TBODY 8.62E-0 57 Quarter 1.13E+00 7.66E-05 1.50E+00 5.74E-05 Annual ADULT TBODY 7.05E-0)5 Annual 2.25E+00 3. 13E-03 3.00OE+00 2.35E-03 F-1.6 146 of 206

Table 3.3-1 10CFR20.1301(a)(1) Compliance Assessment Quad Cities Station Unit One and Unit Two Assessment Period 01/01/05 THROUGH 12/31/05 10CFR20.1301(a)(1) Limit 100.0 mrem/year Quad Cities Unit 1 iSt 2 In 3r 4t Year % of Quarter Quarter Quarter Quarter Total Limit TEDE 1.06E+00 6.52E-01 9.35E-01 6.55E-01 3.30E+00 3.30

-(mrem) _ _ _ _

Quad Cities Unit 2 1 st 2 nd 3 rd 4 th Year % of Quarter Quarter Quarter Quarter Total Limit TEDE 9.42E-01 8.51E-01 9.90E-01 6.49E-01 3.43E+00 3.43 F-1.7 147 of 206

Table 3.4-1 Maximum Doses Resulting From Airborne Releases Based on Concurrent Meteorological Data Quad Cities Station - Unit 1 2005 TYPE OF DOSE FIRST QUARTER SECOND QUARTER THIRD QUARTER FOURTH QUARTER ANNUAL GAMMA AIR (mrad) 2.752E-03(WNW) 3.885E-04( N ) 6.650E-04( N ) 7.050E-04( E ) 3.894E-03(WNW)

BETA AIR (mrad) 4.322E-04( SE) 7.050E-05(NNE) 1.015E-04(NNE) 1.260E-04( E ) 5.997E-04( SE)

WHOLE BODY (mrem) 1.720E-03(SSE) 1.920E-02(NNE) 8.562E-03(NNE) 2.583E-03(NNE) 3.186E-02(NNE)

SKIN (mrem) 2.245E-03(SSE) 2.265E-02(NNE) 1.016E-02(NNE) 3.077E-03(NNE) 3.776E-02(NNE)

ORGAN (mrem) 3.156E-04(WNW) 8.333E-04(WNW) 5.248E-04(WNW) 1.636E-04(WNW) 1.837E-03(WNW)

CRITICAL PERSON Teenager Teenager Teenager Teenager Teenager CRITICAL ORGAN Lung Lung Lung Lung Lung COMPLIANCE STATUS 10 CFR 50 APP. I 10 CFR 50 APP.I TYPE OF DOSE QUARTERLY OBJECTIVE % OF APP. I YEARLY OBJECTIVE % OF APP. I GAMMA AIR (mrad) 5.0 0.06 10.0 0.04 BETA AIR (mrad) 10.0 0.00 20.0 0.00 WHOLE BODY (mrem) 2.5 0.77 5.0 0.64 SKIN (mrem) 7.5 0.30 15.0 0.25 ORGAN (mrem) 7.5 0.01 15.0 0 .01 CRITICAL PERSON Teenager Teenager CRITICAL ORGAN Lung Lung Calculation used release data from the following:

Unit 0 - Vent Unit 0 - Chimney Date of calculation: 4/20/2006 F-1.8 148 of 206

Table 3.4-1 (continued)

Maximum Doses Resulting From Airborne Releases Based on Concurrent Meteorological Data Quad Cities Station - Unit 2 2005 TYPE OF DOSE FIRST QUARTER SECOND QUARTER THIRD QUARTER FOURTH QUARTER ANNUAL GAMMA AIR (mrad) 2.752E-03(WNW) 3.885E-04( N ) 6.650E-04( N ) 7.050E-04( E ) 3.894E-03(WNW)

BETA AIR (mrad) 4.322E-04( SE) 7.050E-05(NNE) 1.015E-04(NNE) 1.260E-04( E ) 5.997E-04( SE)

WHOLE BODY (mrem) 1.720E-03(SSE) 1.920E-02(NNE) 8.562E-03(NNE) 2.583E-03(NNE) 3.186E-02(NNE)

SKIN (mrem) 2.245E-03(SSE) 2.265E-02 (NNE) 1.016E-02(NNE) 3.077E-03(NNE) 3.776E-02(NNE)

ORGAN (mrem) 3.156E-04(WNW) 8.333E-04(WNW) 5.248E-04(WNW) 1.636E-04(WNW) 1.837E-03(WNW)

CRITICAL PERSON Teenager Teenager Teenager Teenager Teenager CRITICAL ORGAN Lung Lung Lung Lung Lung COMPLIANCE STATUS 10 CFR 50 APP. I 10 CFR 50 APP.I TYPE OF DOSE QUARTERLY OBJECTIVE % OF APP. I YEARLY OBJECTIVE % OF APP. I GAMMA AIR (mrad) 5.0 0.06 10.0 0.04 BETA AIR (mrad) 10.0 0.00 20.0 0 .00 WHOLE BODY (mrem) 2.5 0.77 5.0 0.64 SKIN (mrem) 7.5 0.30 15.0 0.25 ORGAN (mrem) 7.5 0.01 15.0 0.01 CRITICAL PERSON Teenager Teenager CRITICAL ORGAN Lung Lung Calculation used release data from the following: Data Recovery 98.9%

Unit 0 - Vent (priority parameters)

Unit 0 - Chimney Date of calculation: 4/20/2006 F-1.9 149 of 206

APPENDIX G METEOROLOGICAL DATA 150 of 206

Quad Cities Nuclear Station Period of Record: January - March 2005 Stability Class - Extremely Unstable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_____ __ __ _ ----- --

0-- --

0-- - - -- -

N 0 6 0 0 0 0 6 0

NNE 0 0

NE 0 5 0 0 0 5 0

ENE 0 8 2 0 0 10 0

E 2 5 0 0 0 7 0

ESE 0 8 0 0 0 8 0

SE 1 1 0 0 0 2 0

SSE 5 6 0 0 0 11 0

S 0 5 0 0 0 5 00 SSW 8 0 0 0 0 8 0

SW 3 1 0 0 0 4 0

WSW 1 3 0 0 0 4 0

W 14 15 2 0 0 31 0

WNW 7 14 3 0 0 24 0

NW 10 13 0 0 0 23 0

NNW 9 8 0 0 0 17 0

Variable 0 0 0 0 0 0 Total 0 66 92 7 0 0 165 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 151 of 206

Quad Cities Nuclear Station Period of Record: January - March 2005 Stability Class - Moderately Unstable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_____ _____ - - - -__- - _--

N 0 4 1 0 0 0 NNE 1 0 0 0 0 NE 0 0 0 0 0 ENE 0 0 1 0 0 E 0 3 0 0 0 ESE 1 3 0 0 0 SE 2 0 0 0 0 SSE 2 1 0 0 0 S 1 1 0 0 00 0 SSW 0 0 0 0 0 SW 3 0 0 0 0 WSW 3 4 0 0 0 W 3 5 0 0 0 WNW 4 4 0 0 0 NW 4 1 0 0 0 NNW 2 0 0 0 0 Variable 0 0 0 Total 0 30 23 1 0 0 54 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 152 of 206

Quad Cities Nuclear Station Period of Record: January - March 2005 Stability Class - Slightly Unstable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_ _ _- - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -

N 4 1 6 NNE 1 0 1 NE 3 1 4 ENE 1 1 5 E 3 0 5 ESE 4 5 10 SE 1 1 2 SSE 5 2 7 S 2 0 2 SSW 2 0 2 SW 5 0 5 WSW 6 1 8 W 4 3 7 WNW 7 11 19 NW 14 7 22 NNW 12 1 14 Variable 0 0 0 Total 5 74 34 6 0 0 119 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 153 of 206

Quad Cities Nuclear Station Period of Record: January - March 2005 Stability Class - Neutral - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_____

N 12 22 9 3 0 0 46 NNE 5 13 8 0 0 0 26 NE 7 50 31 2 0 0 90 ENE 9 42 18 2 0 0 71 E 7 21 18 1 0 0 47 ESE 7 41 20 5 0 0 73 SE 7 19 11 0 0 0 37 SSE 7 10 4 0 0 0 21 S 10 9 1 0 0 0 20 SSW 4 10 6 0 0 0 20 SW 2 25 8 1 0 0 36 WSW 3 28 10 4 0 0 45 W 11 34 23 8 0 0 76 WNW 6 87 63 13 0 0 169 NW 6 83 47 1 0 0 137 NNW 7 45 15 0 0 0 67 Variable 0 0 0 0 0 0 0 Total 110 539 292 40 0 0 981 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 154 of 206

M Quad Cities Nuclear Station Period of Record: January - March 2005 Stability C'lass - SliqhtlV Stable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_________ _ _ _ _ _- - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -

N 7 19 3 0 0 0 29 NNE 8 29 13 1 0 0 51 NE 13 28 13 2 0 0 56 ENE 7 28 4 0 0 0 39 E 15 20 10 0 0 0 45 ESE 14 29 2 0 0 0 45 SE 8 6 5 0 0 0 19 SSE 3 7 1 0 0 0 11 S 6 8 0 0 0 0 14 SSW 4 4 7 0 0 0 15 SW 6 17 S 3 0 0 31 WSW 10 27 6 0 0 0 43 W 10 10 1 0 0 0 21 WNW 9 27 2 0 0 0 38 NW 6 23 0 0 0 0 29 NNW 14 18 0 0 0 0 32 Variable 0 0 0 0 0 0 0 Total 140 300 72 6 0 0 518 Hours of calm in this stability class: 0 Hours of missing wind measurements in this sta.bility class: 0 Hours of missing stability measurements in all stability classes: 0 155 of 206

Quad Cities Nuclear Station Period of Record: January - March 2005 Stability Class - Moderately Stable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total N 0 2 2 0 0 0 0 NNE 2 0 2 0 0 0 0 NE 2 2 4 0 0 0 0 ENE 7 0 7 0 0 0 0 E 7 2 9 0 0 0 0 ESE 16 1 17 0 0 0 0 SE 6 3 9 0 0 0 0 SSE 7 8 15 0 0 0 0 S 5 0 0 0 0 0 5 0 0 0 0 SSW 4 0 4 0 0 0 0 SW 4 1 5 0 0 0 0 WSW 3 0 3 0 0 0 0

W 7 0 7 0 0 0 0 WNW 5 1 6 0 0 0 0 NW 3 2 5 0 0 0 0 NNW 1 0 1 0 0 0 0 Variable 0 0 0 Total 79 22 0 0 0 0 101 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 156 of 206

Quad Cities Nuclear Station Period of Record: January - March 2005 Stability Class - Extremely Stable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_ _ _ - - - - - - - - - - - - - - - _____ - - - -__- - _--

N 0 0

NNE 1 0

NE 2 0

ENE 3 0

E 7 0

ESE 15 0

SE 5 0

SSE 4 0

S 0o 6 0

SSW 6 0

SW 6 0

WSW 2 0

W 1 0

WNW 3 0

NW 1 0

NNW 0 0

Variable 0 Total 49 13 0 0 0 0 62 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 157 of 206

Quad Cities Nuclear Station Period of Record: January - March 2005 Stability Class - Extremely Unstable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in 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 0 0 0 0 0 NE 0 0 0 0 0 0 0 ENE 0 0 0 2 0 0 2 E 0 0 1 0 0 0 1 ESE 0 0 1 1 0 0 2 SE 0 0 0 0 0 0 0 SSE 0 0 0 0 0 0 0 S 0 0 0 0 2 1 3 SSW 0 1 3 1 0 0 5 SW 0 0 1 0 0 0 1 WSW 0 0 0 0 0 0 0 W 0 0 4 3 0 0 7 WNW 0 0 1 0 0 0 1 NW 0 0 1 5 0 0 6 NNW 0 0 3 0 0 0 3 Variable 0 0 0 0 0 0 0 Total 0 1 15 12 2 1 31 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 77 158 of 206

Quad Cities Nuclear Station Period of Record: January - March 2005 Stability Class - Moderately Unstable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

__

1__ --

0-- --

0-- -----

N 1 0 0 0 0 1 NNE NE 0 2 1 0 0 3 ENE 0 0 0 0 1 1 E 0 3 1 0 0 4 ESE 0 0 1 0 0 1 SE 0 1 1 0 0 2 SSE 3 0 0 1 0 4 S 0 0 0 0 2 2 SSW 1 1 0 0 0 2 SW 0 2 0 0 0 2 WSW 2 1 1 1 0 5 W 1 11 4 0 0 16 WNW 0 3 2 8 1 14 NW 1 4 2 2 0 9 NNW 1 4 0 0 0 5 Variable 0 0 0 0 0 0 Total 0 10 32 13 12 4 71 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 3 Hours of missing stability measurements in all stability classes: 77 159 of 206

Quad Cities Nuclear Station Period of Record: January - March 2005 Stability Class - Slightly Unstable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total N 0 2 2 0 0 0 4 0

NNE 1 0 0 0 0 1 0

NE 0 1 0 0 0 1 0

ENE 0 1 0 1 1 3 0

E 0 5 0 0 0 5 0

ESE 0 4 0 0 0 4 0

SE 0 2 1 0 0 3 0

SSE 1 0 2 3 0 6 0

S 2 1 0 0 1 4 00 SSW 0 2 0 0 0 2 0

SW 2 2 0 0 0 4 0

WSW 4 1 5 1 0 11 0

W 4 4 5 0 1 14 0

WNW 1 6 2 6 1 16 0

NW 1 7 3 2 0 13 0

NNW 5 2 0 0 0 7 0

Variable 0 0 0 0 0 0 Total 0 23 40 18 13 4 98 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 1 Hours of missing stability measurements in all stability classes: 77 160 of 206

Quad Cities Nuclear Station Period of Record: January - March 2005 Stability Class - Neutral - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_ _ _- - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -

N 3 19 22 5 2 2 53 NNE 2 21 16 4 0 0 43 NE 4 17 33 41 13 0 108 ENE 2 8 22 23 6 5 66 E 5 13 11 19 4 0 52 ESE 9 11 17 22 10 5 74 SE 5 9 10 25 3 0 52 SSE 3 7 10 5 5 7 37 S 1 5 4 6 2 3 21 SSW 3 5 6 6 8 2 30 SW 0 4 10 8 3 3 28 WSW 0 6 11 13 7 3 40 W 0 2 23 15 12 9 61 WNW 0 19 33 33 22 20 127 NW 1 20 61 64 37 3 186 NNW 3 17 39 29 7 0 95 Variable 0 0 0 0 0 0 0 Total 41 183 328 318 14 1 62 1073 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 35 Hours of missing stability measurements in all stability classes: 77 161 of 206

Quad Cities Nuclear Station Period of Record: January - March 2005 Stability Class - Slightly Stable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total N 2 5 12 4 0 0 23 NNE 0 13 21 5 0 0 39 NE 0 7 19 10 0 0 36 ENE 1 6 19 15 2 0 43 E 4 14 15 12 3 0 48 ESE 2 7 11 33 2 0 55 SE 0 4 18 10 0 1 33 SSE 0 6 6 7 6 5 30 S 1 3 9 5 2 0 20 SSW 0 1 2 5 2 8 18 SW 0 1 6 16 3 4 30 WSW 0 3 4 14 5 0 26 W 0 2 14 6 3 1 26 WNW 0 3 14 7 2 0 26 NW 1 3 17 25 3 0 49 NNW 0 5 11 15 1 0 32 Variable 0 0 0 0 0 0 0 Total 11 83 198 189 34 19 534 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 34 Hours of missing stability measurements in all stability classes: 77 162 of 206

Quad Cities Nuclear Station Period of Record: January - March 2005 Stability Class - Moderately Stable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total N 1 2 2 1 0 0 6 NNE 0 0 3 1 0 0 4 NE 1 2 3 0 0 0 6 ENE 0 3 0 1 0 0 4 E 0 1 1 1 0 0 3 ESE 0 4 9 3 0 0 16 SE 0 3 14 2 0 0 19 SSE 0 0 4 4 3 0 11 S 0 0 15 14 2 0 31 SSW 0 1 1 8 2 0 12 SW 0 3 4 2 0 0 9 WSW 0 3 1 3 0 0 7 W 0 1 2 0 0 0 3 WNW 0 0 2 0 0 0 2 NW 0 4 3 1 0 0 8 NNW 0 1 1 1 0 0 3 Variable 0 0 0 0 0 0 0 Total 2 28 65 42 7 0 144 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 2 Hours of missing stability measurements in all stability classes: 77 163 of 206

Quad Cities Nuclear Station Period of Record: January - March 2005 Stability Class - Extremely Stable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total N 0 1 0 0 0 0 1 NNE 0 0 0 0 0 0 0 NE 0 0 1 0 0 0 1 ENE 1 1 1 0 0 0 3 E 0 0 0 0 0 0 0 ESE 0 1 2 1 0 0 4 SE 0 0 3 2 0 0 5 SSE 0 1 2 0 0 0 3 S 0 0 4 8 1 0 13 SSW 2 3 5 8 1 0 19 SW 0 1 0 0 0 0 1 WSW 2 0 1 0 0 0 3 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 2 0 2 0 0 4 NNW 0 0 0 0 0 0 0 Variable 0 0 0 0 0 0 0 Total 5 10 19 21 2 0 57 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability cl,asses: 77 164 of 206

Quad Cities Nuclear Station Period of Record: April - June 2005 Stability Class - Extremely Unstable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_________ _ _ _- - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -

N 0 0 4 0 5 NNE 0 11 4 0 16 NE 0 2 6 0 14 ENE 0 3 4 0 7 E 0 5 8 0 13 ESE 0 2 14 0 16 SE 0 8 11 0 19 SSE 0 29 9 0 38 S 0 13 9 0 22 SSW 0 26 17 0 43 SW 0 28 14 0 42 WSW 0 4 17 0 21 W 0 9 17 0 29 WNW 0 11 31 0 42 NW 0 5 4 0 12 NNW 0 7 5 0 20 Variable 0 0 0 0 0 Total 0 163 174 22 0 0 359 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 165 of 206

Quad Cities Nuclear Station Period of Record: April - June 2005 Stability Class - Moderately Unstable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

. _ - _ _

-_ _ _ _ _ _ - - - - -

N 0 2 0 0 0

NNE 0 4 0 0

NE 0 1 0 0

ENE 0 1 0 0

E 0 0 0 0

ESE 0 2 0 0

SE 0 6 0 0

SSE 0 2 0 0

S 0 6 0 00 SSW 0 5 0 0

SW 0 4 0 0

WSW 0 0 0 0

W 0 3 3 0

WNW 0 2 0 0

NW 0 3 0 0

NNW 0 1 0 0

Variable 0 0 0 Total 0 42 26 3 0 0 71 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 166 of 206

- -

-4 Quad Cities Nuclear Station Period of Record: April - June 2005 Stability Class - Slightly Unstable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total N 0 3 0 0 0 0 3 NNE 0 3 3 0 0 0 6 NE 0 2 7 0 0 0 9 ENE 0 1 1 0 0 0 2 E 0 5 4 0 0 0 9 ESE 0 6 4 0 0 0 10 SE 0 6 2 0 0 0 8 SSE 1 6 0 0 0 0 7 S 0 8 0 0 0 0 8 SSW 1 13 0 0 0 0 14 SW 0 10 2 0 0 0 12 WSW 0 5 5 0 0 0 10 W 0 10 4 0 0 0 14 WNW 0 7 4 4 0 0 15 NW 1 2 3 0 0 0 6 NNW 0 5 2 1 0 0 8 Variable 0 0 0 0 0 0 0 Total 3 92 41 5 0 0 141 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 167 of 206

Quad Cities Nuclear Station Period of Record: April - June 2005 Stability Class - Neutral - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total N 1 10 5 5 0 0 21 NNE 2 7 11 0 0 0 20 NE 3 10 25 0 0 0 38 ENE 6 19 31 0 0 0 56 E 4 10 10 2 0 0 26 ESE 1 21 6 5 0 0 33 SE 5 21 5 0 0 0 31 SSE 3 18 2 0 0 0 23 S 5 13 0 0 0 0 18 SSW 5 26 2 0 0 0 33 SW 10 34 7 1 0 0 52 WSW 7 26 16 1 0 0 50 W 4 36 23 1 0 0 64 WNW 2 22 30 1 0 0 55 NW 4 12 10 0 0 0 26 NNW 0 7 9 1 0 0 17 Variable 0 0 0 0 0 0 0 Total 62 292 192 17 0 0 563 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 168 of 206

n Quad Cities Nuclear Station Period of Record: April - June 2005 Stability Class - Slightly Stable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total N 4 5 0 0 0 0 9 NNE 1 4 3 0 0 0 8 NE 2 8 5 0 0 0 15 ENE 20 8 0 0 0 0 28 E 12 20 5 3 0 0 40 ESE 11 34 7 0 0 0 52 SE 18 34 4 1 0 0 57 SSE 15 7 2 0 0 0 24 S 10 19 0 0 0 0 29 SSW 9 17 0 0 0 0 26 SW 10 40 9 1 0 0 60 WSW 16 27 2 0 0 0 45 W 22 28 1 0 0 0 51 WNW 18 22 3 0 0 0 43 NW 13 20 8 0 0 0 41 NNW 3 11 2 0 0 0 16 Variable 0 0 0 0 0 0 0 Total 184 304 51 5 0 0 544 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 169 of 206

x Quad Cities Nuclear Station Period of Record: April - June 2005 Stability Class - Moderately Stable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_________ _____ _____ _____ _____

N 7 0 0 0 7 0

NNE 9 5 0 0 14 0

NE 9 3 0 0 12 0

ENE 10 4 0 0 14 0

E 17 3 1 0 21 0

ESE 25 30 1 0 56 0

SE 18 4 0 0 22 0

SSE 11 6 1 0 18 0

S 12 6 0 0 18 0

0 SSW 14 6 0 0 20 0

SW 8 2 0 0 10 0

WSW 4 0 0 0 4 0

W 9 1 0 0 10 0

WNW 9 0 0 0 9 0

NW 4 1 0 0 5 0

NNW 0 0 0 0 0 0

Variable 0 0 0 0 0 0

Total 166 71 3 . 0 240 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 170 of 206

Quad Cities Nuclear Station Period of Record: April - June 2005 Stability Class - Extremely Stable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total N 4 0 4 0 0 0 0 NNE 4 1 5 0 0 0 0 NE 3 0 3 0 0 0 0 ENE 9 0 9 0 0 0 0 E 18 5 23 0 0 0 0 ESE 29 16 45 0 0 0 0 SE 10 0 10 0 0 0 0 SSE 8 1 9 0

__ _ _ _ 0_ _ _ 0_ _ _ 0_

S 3 0 3 0 0 0 0 SSW 8 0 8 0 0 0 0 SW 9 0 9 0 0 0 0 WSW 1 0 1 0 0 0 0 W 5 1 6 0 0 0 0 WNW 5 1 6 0 0 0 0 NW 2 0 2 0 0 0 0 NNW 0 0 0 0 0 0 0 Variable 0 0 0 Total 118 25 0 0 0 0 143 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 171 of 206

Quad Cities Nuclear Station Period of Record: April - June 2005 Stability Class - Extremely Unstable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_________ _____ _ _ _ _ _ - - - - - - - - - - - - - - - - - - - - - - - - -

N 0 1 0 0 0 1 0

NNE 0 3 1 0 0 4 0

NE . 0 0 1 5 0 6 0

ENE 0 0 0 0 0 0

0 E 0 0 2 0 0 2 ESE 0 0 0 9 0 0 '9 SE 0 0 3 5 0 0 8 SSE 0 0 4 11 3 1 19 S 0 0 2 13 4 0 19 SSW 0 1 10 17 8 0 36 SW 0 2 3 7 0 0 12 WSW 0 0 2 5 2 0 9 W 0 0 4 3 0 0 7 WNW 0 1 4 13 3 0 21 NW 0 0 3 0 5 1 9 NNW 0 0 1 0 6 1 8 Variable 0 0 0 0 0 0 0 Total 0 4 40 87 36 3 170 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 49 172 of 206

Quad Cities Nuclear Station Period of Record: April - June 2005 Stability Class - Moderately Unstable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_________ _____ _ _ _ _ _ - - - - - - - - - - - - - - - - - - - - - - - - -

N 0 3 0 0 0 3 0

NNE 0 7 2 0 0 9 0

NE 1 2 4 2 0 9 0

ENE 0 0 0 0 0 0 0 0

E 1 7 4 0 0 12 0

ESE 0 3 3 0 0 6 0

SE 1 2 3 1 0 7 SSE 0 6 6 4 1 0 17 S 0 2 2 1 3 0 8 SSW 0 8 4 7 1 1 21 SW 0 2 4 5 1 1 13 WSW 0 2 2 3 0 0 7 W 0 1 3 4 3 1 12 WNW 0 0 4 6 5 0 15 NW 0 0 4 1 0 0 5 NNW 0 1 5 0 3 1 10 Variable 0 0 0 0 0 0 0 Total 0 25 58 47 20 4 154 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 49 173 of 206

Quad Cities Nuclear Station Period of Record: April - June 2005 Stability Class - Slightly Unstable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total N 0 7 0 0 1 0 8 NNE 0 3 3 0 0 0 6 NE 0 3 0 5 3 0 11 ENE 0 1 2 0 0 0 3 E 0 0 10 1 0 0 11 ESE 1 2 6 3 0 0 12 SE 0 3 7 1 0 0 11 SSE 0 9 7 3 0 1 20 S 0 6 5 1 1 0 13 SSW 0 8 3 5 4 2 22 SW 0 7 2 3 1 0 13 WSW 0 3 2 2 0 0 7 W 0 1 3 7 2 1 14 WNW 0 3 3 9 7 0 22 NW 0 1 2 6 2 0 11 NNW 1 2 1 3 2 0 9 Variable 0 0 0 0 0 0 0 Total 2 59 56 49 23 4 193 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 1 Hours of missing stability measurements in all stability classes: 49 174 of 206

R Quad Cities Nuclear Station Period of Record: April - June 2005 Stability Class - Neutral - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

-____ _____

N 0 7 3 5 6 0 21 NNE 1 2 6 9 4 0 22 NE 1 6 6 19 14 1 47 ENE 3 7 8 19 11 1 49 E 0 8 10 9 11 1 39 ESE 0 5 14 10 6 6 41 SE 1 6 13 7 8 1 36 SSE 0 6 6 7 4 0 23 S 2 9 8 18 6 1 44 SSW 2 17 12 12 5 0 48 SW 3 9 11 17 2 2 44 WSW 1 6 11 9 13 1 41 W 1 6 6 30 25 4 72 WNW 1 3 7 47 13 10 81 NW 0 4 5 7 11 1 28 NNW 2 9 2 10 8 0 31 Variable 0 0 0 0 0 0 0 Total 18 110 128 235 147 29 667 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 1 Hours of missing stability measurements in all stability classes: 49 175 of 206

Quad Cities Nuclear Station Period of Record: April - June 2005 Stability Class - Slightly Stable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total N 1 1 7 4 0 0 13 NNE 0 3 2 2 0 0 7 NE 0 1 5 11 4 0 21 ENE 2 1 7 1 0 0 11 E 1 1 14 13 4 0 33 ESE 1 2 16 18 5 1 43 SE 0 3 16 35 7 0 61 SSE 0 4 15 17 6 0 42 S 1 2 23 23 7 0 56 SSW 0 0 12 37 3 0 52 SW 0 4 7 26 3 0 40 WSW 1 3 7 21 4 0 36 W 0 4 10 21 1 0 36 WNW 0 5 9 12 2 1 29 NW 1 5 16 10 6 1 39 NNW 1 6 12 15 1 0 35 Variable 0 0 0 0 0 0 0 Total 9 45 178 266 53 3 554 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 1 Hours of missing stability measurements in all stability classes: 49 176 of 206

Quad Cities Nuclear Station Period of Record: April - June 2005 Stability Class - Moderately Stable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

__

1__ --

0-- --

0--

N 2 1 0 0 0 4 11 NNE 0 1 1

NE 3 5 8 0 0 17 1

ENE 2 6 4 0 0 13 1

E 4 9 2 0 0 16 1

ESE 3 17 23 9 0 53 SE 0 1 12 30 4 0 47 SSE 1 1 5 7 4 0 18 S 0 1 10 22 3 0 36 SSW 0 2 8 18 0 0 28 SW 1 3 2 8 0 0 14 WSW 0 1 0 2 0 0 3 W 0 1 2 6 0 0 9 WNW 1 1 2 4 0 0 8 NW 0 4 7 0 0 0 11 NNW 1 4 3 0 0 0 8 Variable 0 0 0 0 0 0 0 Total 10 33 89 134 20 0 286 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 49 177 of 206

Quad Cities Nuclear Station Period of Record: April - June 2005 Stability Class - Extremely Stable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

- - - - - - - - - - - - - -__- - _--

N 1 0 2 2 0 5 NNE 0 0 0 0 0 0 NE 0 0 0 0 0 0 ENE 0 2 6 0 0 8 E 0 0 2 0 0 2 ESE 0 0 2 2 0 6 SE 1 1 1 8 0 13 SSE 0 0 6 5 0 11 S 1 0 5 15 0 21 SSW 0 1 6 6 0 13 SW 0 4 3 4 0 11 WSW 6 2 0 0 0 8 W 1 2 0 0 0 3 WNW 0 0 0 0 0 0 NW 1 0 2 0 0 3 NNW 1 3 0 0 0 4 Variable 0 0 0 0 0 0 Total 12 15 35 42 0 108 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 49 178 of 206

Quad Cities Nuclear Station Period of Record: July - September 2005 Stability Class - Extremely Unstable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_________ _____ _ _ _ _ _ - - - - - - - - - - - - - - - - - - - - - - - - -

N 0 7 8 0 0 0 15 NNE 0 4 9 0 0 0 13 NE 0 14 13 0 0 0 27 ENE 0 4 2 0 0 0 6 E 1 3 7 0 0 0 11 ESE 0 3 7 0 0 0 10 SE 0 13 4 0 0 0 17 SSE 0 39 1 0 0 0 40 S 0 15 3 0 0 0 18 SSW 0 42 7 0 0 0 49 SW 0 31 8 0 0 0 39 WSW 0 10 5 0 0 0 15 W 0 6 4 0 0 0 10 WNW 0 10 1 0 0 0 11 NW 0 21 6 0 0 0 27 NNW 0 12 2 0 0 0 14 Variable 0 0 0 0 0 0 0 Total 1 234 87 0 0 0 322 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 179 of 206

Quad Cities Nuclear Station Period of Record: July - September 2005 Stability Class - Moderately Unstable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

__

1__ --

0-- --

0--

N 0 4 1 0 0 0 5 0

NNE 5 1 0 0 0 6 0

NE 2 0 0 0 0 2 0

ENE 3 3 0 0 0 0 0 E 0 0 0 0 0 0 0 ESE 3 3 0 0 0 0 0 SE 2 2 0 0 0 0 0 SSE 4 4 0 0 0 0 0 S 5 5 00 0 0 0 0 SSW 4 4 0 00 0

.0 00 00 SW 8 8 0 0 .0 0 0 WSW 2 2 0 0 0 0 0 W 2 2 0 0 0 0 0 WNW 6 6 0 0 0 0 0 NW 8 8 0 0 0 0 0 NNW 7 7 0 0 0 0 0 Variable 0 0 Total 0 65 2 0 0 0 67 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 180 of 206

Quad Cities Nuclear Station Period of Record: July - Septembe r 2005 Stability Class - Slightly Unstable - 196 Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind DirectiorI 1-3 4-7 8-12 13-18 19-24 > 24 Total

- - - - - - - - - - - _--

__

N 0 14 1 0 0 15 NNE 0 6 0 0 0 6 NE 0 12 1 0 0 13 ENE 2 11 1 0 0 14 E 0 1 2 0 0 3 ESE 0 2 0 0 0 2 SE 0 9 1 0 0 10 SSE 2 5 0 0 0 7 S 0 10 0 0 0 10 SSW 2 14 3 0 0 19 SW 1 16 0 0 0 17 WSW 0 10 0 0 0 10 W 0 16 2 0 0 18 WNW 0 5 0 0 0 5 NW 0 14 1 0 0 15 NNW 0 10 0 0 0 10 IVariable 0 0 0 0 0 0 Total 7 155 12 0 0 0 174 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 181 of 206

Quad Cities Nuclear Station Period of Record: July - September 2005 Stability Class - Neutral - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total N .2 33 17 0 52 0

NNE 1 19 3 0 23 0

NE 4 22 6 0 32 0

ENE 6 25 2 0 33 0

E 2 16 1 0 19 0

ESE 4 33 2 0 39 0

SE 4 13 1 0 18 0

SSE 5 14 0 0 19 0

S 7 16 0 0o 0 23 0

SSW 4 20 3 0 27 0

SW 5 23 5 0 33 0

WSW 8 23 1 0 32 0

W 5 14 3 0 22 0

WNW 6 19 2 0 27 0

NW 6 29 6 0 41 0

NNW 5 24 4 0 33 0

Variable 0 0 0 0 0 Total 74 343 56 0 0 0 473 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 182 of 206

Quad Cities Nuclear Station Period of Record: July - September 2005 Stability Class - Slightly Stable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total N 8 31 0 39 NNE 17 14 0 31 NE 11 19 0 30 ENE 11 12 0 23 E 13 5 0 18 ESE 12 23 0 35 SE 19 8 0 27 SSE 16 5 0 23 S 14 31 0 46 SSW 5 16 0 22 SW 7 23 0 31 WSW 12 18 0 30 W 14 16 0 30 WNW 16 21 0 38 NW 6 27 0 33 NNW 6 29 0 36 Variable 0 0 0 0

/

Total 187 298 6 1 0 492 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 183 of 206

Quad Cities Nuclear Station Period of Record: July - September 2005 Stability Class - Moderately Stable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_ _ _ _ - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -

N 13 3 0 16 NNE 14 0 0 14 NE 10 3 0 13 ENE 12 1 0 13 E 16 2 0 18 ESE 28 10 0 38 SE 26 0 0 26 SSE 35 1 0 36 S 16 9 0 25 SSW 8 8 0 16 SW 3 0 0 3 WSW 9 1 0 10 W 4 2 0 6 WNW 14 2 0 16 NW 12 1 0 13 NNW 9 1 0 10 Variable 0 0 0 0 Total 229 V 44 0 273 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 184 of 206

Quad Cities Nuclear Station Period of Record: July - September 2005 Stability Class - Extremely Stable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_________ _____ _ _ _ _ _ - - - - - - - - - - - - - - - - - - - - - - - - -

N 3 0 0 0 0 0 3 NNE 5 0 0 0 0 0 5 NE 6 2 0 0 0 0 8 ENE 3 0 0 0 0 0 3 E 28 0 0 0 0 0 28 ESE 73 0 75 SE 33 0 33 SSE 18 0 18 S 10 0 10 SSW 0 0 0 SW 2 0 2 WSW 0 0 0 W 7 0 7 WNW 13 0 13 NW 3 0 3 NNW 4 0 4 Variable 0 0 0 Total 208 0 212 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 185 of 206

Quad Cities Nuclear Station Period of Record: July - September 2005 Stability Class - Extremely Unstable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_ _ _ _ - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -

N 2 0 2 NNE 3 0 3 NE 4 9 13 ENE 2 0 2 E 1 0 1 ESE 0 2 2 SE 3 2 5 SSE 17 6 24 S 2 4 7 SSW 10 28 41 SW 7 .1 9 WSW 1 2 3 W 0 1 1 WNW 0 2 2 NW 3 4 7 NNW 2 2 4 Variable 0 0 0 Total 0 5 57 63 1 0 126 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 32 186 of 206

Quad Cities Nuclear Station Period of Record: July - September 2005 Stability Class - Moderately Unstable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_________ _____ _ _ _ _ _ - - - - - - - - - - - - - - - - - - - - - - - - -

N 1 3 3 0 0 7 0

NNE 2 5 1 0 0 8 0

NE 3 5 2 0 0 10 00 ENE 3 1 1 0 0 5 0

E 2 4 1 0 0 7 0

ESE 0 1 1 0 0 2 SE 0 1 6 2 1 0 10 SSE 0 0 6 3 2 0 11 S 0 2 4 5 1 0 12 SSW 0 2 7 4 1 0 14 SW 0 2 0 1 0 0 3 WSW 0 1 1 3 0 0 5 W 0 3 0 4 0 0 7 WNW 0 1 5 4 0 0 10 NW 0 2 8 3 0 0 13 NNW 0 2 11 0 0 14 Variable 0 0 0 0 0 0 0 Total 0 27 67 39 5 0 138 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 32 187 of 206

Quad Cities Nuclear Station Period of Record: July - September 2005 Stability Class - Slightly Unstable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

-____ - - - - - - - - - - - - - - -

__ - _--

N 0 6 8 0 15 NNE 0 2 7 0 9 NE 0 8 8 0 17 ENE 1 1 6 0 9 E 0 1 4 0 6 ESE 0 1 1 0 4 SE 0 4 4 0 9 SSE 0 7 6 0 16 S 0 3 5 0 11 SSW 0 10 10 0 28 SW 0 10 5 0 17 WSW 0 4 1 0 8 W 0 9 1 0 11 WNW 0 7 1 0 11 NW 0 14 6 0 22 NNW 0 9 6 0 15 Variable 0 0 0 0 0 Total 1 96 79 29 3 0 208 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 32 188 of 206

Quad Cities Nuclear Station Period of Record: July - September 2005 Stability Class - Neutral - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total N 1 20 16 21 2 0 60 NNE 2 9 10 10 0 0 31 NE 3 14 14 10 0 0 41 ENE 3 10 13 3 0 0 29 E 1 3 13 6 0 0 23 ESE 0 2 16 15 0 0 33 SE 0 6 10 2 2 0 20 SSE 0 9 8 6 0 0 23 S 1 10 11 12 3 0 37 SSW 0 12 15 15 8 0 50 SW 1 10 16 7 3 0 37 WSW 0 14 10 15 0 0 39 W 1 9 2 9 2 0 23 WNW 1 15 7 7 3 0 33 NW 4 6 21 12 3 2 48 NNW 1 14 13 10 1 1 40 Variable 0 0 0 0 0 0 0 Total 19 163 195 160 27 3 567 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 32 189 of 206

Quad Cities Nuclear Station Period of Record: July - September 2005 Stability Class - Slightly Stable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

._ _ _ - - - - - - - - - - - - - - - - - - - - - - - - - _____

N 0 6 20 22 0 0 48 NNE 2 6 22 18 0 0 48 NE 0 3 13 16 0 0 32 ENE 0 4 22 3 0 0 29 E 1 6 7 6 0 0 20 ESE 0 3 9 17 2 0 31 SE 2 3 15 15 0 0 35 SSE 0 3 14 14 2 0 33 S 0 3 13 26 8 1 51 SSW 0 0 9 34 10 0 53 SW 1 3 9 11 3 0 27 WSW 1 1 8 5 3 0 18 W 0 0 12 13 0 0 25 WNW 0 2 5 17 0 0 24 NW 0 1 10 21 2 0 34 NNW 0 0 7 16 0 0 23 Variable 0 0 0 0 0 0 0 Total 7 44 195 254 30 1 531 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 5 Hours of missing stability measurements in all stability classes: 32 190 of 206

Quad Cities Nuclear Station Period of Record: July - September 2005 Stability Class - Moderately Stable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_________ _ _ _ - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -

N 4 6 2 0 14 NNE 6 18 7 0 31 NE 4 9 1 0 16 ENE 3 3 4 0 10 E 4 20 3 0 28 ESE 4 17 16 0 38 SE 2 9 14 0 25 SSE 3 13 25 0 43 S 0 12 35 0 51 SSW 2 6 33 0 43 SW 2 3 0 0 6 WSW 2 4 4 0 11 W 0 5 12 0 18 WNW 0 0 6 0 7 NW 1 3 7 0 11 NNW 2 0 2 0 5 Variable 0 0 0 0 0 Total 9 39 128 171 10 0 357 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 6 Hours of missing stability measurements in all stability classes: 32 191 of 206

Quad Cities Nuclear Station Period of Record: July - September 2005 Stability Class - Extremely Stable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total 15---

N 6 7 0 0 0 15 NNE 0 3 0 0 0 NE 1 4 1 0 0 6 ENE 8 4 2 0 0 18 E 4 1 0 0 0 7 ESE 6 10 4 0 0 21 SE 2 4 11 0 0 18 SSE 3 7 12 0 0 22 S 7 16 27 0 0 50 SSW 2 19 16 0 0 39 SW 1 4 3 0 0 9 WSW 2 1 0 0 0 3 W 3 2 1 0 0 8 WNW 1 3 1 0 0 6 NW 1 4 1 0 0 6 NNW 0 3 2 0 0 5 Variable 0 0 0 0 0 0 Total 18 47 92 81 0 0 238 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 32 192 of 206

Quad Cities Nuclear Station Period of Record: October - December2005 Stability Class - Extremely Unstable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_ _ _- - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -

N 0 1 NNE 2 5 NE 4 13 ENE 2 5 E 0 0 ESE 0 2 SE 2 2 SSE 0 0 S 6 7 SSW 18 33-SW 17 21 WSW 2 5 W 5 9 WNW 4 14 NW 4 14 NNW 1 6 Variable 0 0 Total 0 67 63 7 0 0 137 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0

. 193 of 206

Quad Cities Nuclear Station Period of Record: October - December2005 Stability Class - Moderately Unstable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total N 0 1 0 0 0 0 1 0

NNE 0 1 0 0 0 1 0

NE 1 2 0 0 0 3 0

ENE 1 0 0 0 0 1 0

E 0 0 0 0 0 0 0

ESE 0 0 0 0 0 0 0

SE 1 1 0 0 0 2 0

SSE 0 0 0 0 0 0 0

S 2 0 0 0 0 2 00 SSW 5 2 0 0 0 7 0

SW 2 0 0 0 0 2 10 WSW 2 1 0 0 0 3 0

W 1 1 1 0 0 3 0

WNW 0 2 3 0 0 5 0

NW 3 2 0 0 0 5 0

NNW 0 0 0 0 0 0 0

Variable 0 0 0 0 0 0 Total 0 19 12 4 0 0 35 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 194 of 206

Quad Cities Nuclear Station Period of Record: October - December2005 Stability (Class - Slightly Unstable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_____ -____ _ _ _ _ _ - - - - - - - - - - - - - - -

N 4 7 11 0

NNE 1 3 4 0

NE 1 2 3 0

ENE 5 0 5 0

E 3 0 3 0

ESE 1 0 1 0

SE 3 1 4 0

SSE 3 1 4 0

S 0o 3 4 7 0

SSW 3 0 3 0

SW 8 3 11 0

WSW 5 2 7 0

W 15 5 20 0

WNW 6 2 8 0

NW 8 9 18 0

NNW 5 0 6 0

Variable 0 0 0 Total 0 74 39 2 0 0 115 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 195 of 206

Quad Cities Nuclear Station Period of Record: October - December2005 Stability Class - Neutral - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_____ -____ _____

N 7 25 35 1 0 0 68 NNE 5 14 4 0 0 0 23 NE 10 26 10 0 0 0 46 ENE 9 36 9 0 0 0 54 E 6 31 13 0 0 0 50 ESE 7 18 10 0 0 0 35 SE 5 19 23 2 0 0 49 SSE 7 10 6 0 0 0 23 S 1 21 4 0 0 0 26 SSW 4 19 11 0 0 0 34 SW 6 36 22 1 0 0 65 WSW 7 56 35 10 0 0 108 W 11 88 71 30 0 0 200 WNW 3 80 62 22 0 0 167 NW 7 57 13 10 0 0 87 NNW 3 43 8 0 0 0 54 Variable 0 0 0 0 0 0 0 Total 98 579 336 76 0 0 1089 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 196 of 206

Quad Cities Nuclear Station Period of Record: October - December2005 Stability Class - Slightly Stable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total N 4 7 2 0 0 0 13 NNE 5 4 0 0 0 0 9 NE 10 19 2 0 0 0 31 ENE 8 12 1 0 0 0 21 E 7 4 0 1 0 0 12 ESE 8 7 10 2 0 0 27 SE 13 7 6 2 0 0 28 SSE 12 18 1 0 0 0 31 S 5 37 5 0 0 0 47 SSW 3 39 5 1 0 0 48 SW 7 32 15 1 0 0 55 WSW 10 26 2 1 0 0 39 W 16 37 2 0 0 0 55 WNW 4 25 2 0 0 0 31 NW 7 25 0 0 0 0 32 NNW 3 8 2 0 0 0 13 Variable 0 0 0 0 0 0 0 Total 122 307 55 8 0 0 492 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 197 of 206

Quad Cities Nuclear Station Period of Record: October - December2005 Stability Class - Moderately Stable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total N 4 0 4 0 0 0 0 NNE 9 1 10 0 0 0 0 NE 10 1 11 0 0 0 0 ENE 1 3 4 0 0 0 0 E 8 2 10 0 0 0 0 ESE 12 14 26 0 0 0 0 SE 18 3 21 0 0 0 0 SSE 21 5 26 0 0 0 0 S 6 9 15 0 0 0 0 SSW 2 4 6 0 0 0 0 SW 1 1 2 0 0 0 0 WSW 2 0 2 0 0 0 0 W 3 6 9 WNW 3 2 0 0 0 0 5 NW 3 2 0 0 0 0 5 NNW 6 0 0 0 0 0 6 Variable 0 0 0 0 0 0 0 Total 109 53 0 0 0 0 162 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 198 of 206

Quad Cities Nuclear Station Period of Record: October - December2005 Stability Class - Extremely Stable - 196Ft-33Ft Delta-T (F)

Winds Measured at 33 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

- - - - - - - - - - - - - - - - - - - - - _--

__

N 1 0 0 0 0 0 1 NNE 2 0 0 0 0 0 2 NE 6 0 0 0 0 0 6 ENE 5 0 0 0 0 0 5 E 3 0 0 0 0 0 3 ESE 25 9 0 0 0 0 34 SE 14 1 0 0 0 0 15 SSE 10 1 0 0 0 0 11 S 3 0 0 0 0 0 3 SSW 3 0 0 0 0 0 3 SW 3 0 0 0 0 0 3 WSW 1 0 0 0 0 0 1 W 5 0 0 0 0 0 5 WNW 9 1 0 0 0 0 10 NW 5 0 0 0 0 0 5 NNW 0 0 0 0 0 0 0 Variable 0 0 0 0 0 0 0 Total 95 12 0 0 0 0 107 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 199 of 206

Quad Cities Nuclear Station Period of Record: October - December2005 Stability Class - Extremely Unstable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_____

N 0 0 0 0 0 0 0 0 0 NNE 0 0 0 0 0 0 0 NE 0 3 0 0 3 0 0 ENE 2 0 0 0 2 0 0 E 0 0 0 0 0 0 0 ESE 0 0 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE 0 0 0 0 0 0 0 S 0 1 1 0 2 00 00 SSW 1 17 6 0 24 0 0 SW 5 0 0 0 5 0 0 WSW 1 0 0 0 1 0 0 W 0 0 0 0 0 0 0 WNW 0 3 0 0 3 0 0 NW 2 3 0 0 5 0 0 NNW 0 0 0 0 0 0 0 Variable 0 0 0 0 0 Total 0 0 11 27 7 0 45 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 1 200 of 206

Quad Cities Nuclear Station Period of Record: October - December2005 Stability Class - Moderately Unstable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_ _ _ - - - - - - - - - - - - - - - - - - - - - - - - - - - - - -

N NNE NE ENE E

ESE SE SSE S

SSW SW WSW W

WNW NW NNW Variable Total 0 0 25 21 0 5 51 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 1 201 of 206

Quad Cities Nuclear Station Period of Record: October - December2005 Stability Class - Slightly Unstable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total N 0 0 4 1 0 0 5 NNE 0 0 3 2 1 0 6 NE 0 2 1 1 0 0 4 ENE 0 0 4 0 0 0 4 E 0 1 0 0 0 0 1 ESE 0 1 0 0 0 0 1 SE 0 0 1 1 0 0 2 SSE 0 0 3 0 0 0 3 S 0 0 1 4 2 0 7 SSW 0 0 0 14 2 0 16 SW 0 0 3 6 1 0 10 WSW 0 3 4 2 0 0 9 W 0 2 3 1 0 0 6 WNW 0 1 4 4 0 5 14 NW 0 1 6 4 0 0 11 NNW 0 1 3 1 0 1 6 Variable 0 0 0 0 0 0 0 Total 0 12 40 41 6 6 105 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 1 202 of 206

Quad Cities Nuclear Station Period of Record: October - December2005 Stability Class - Neutral - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total N 1 6 17 44 8 1 77 NNE 3 4 11 6 2 0 26 NE 1 6 12 24 1 0 44 ENE 3 7 17 24 1 0 52 E 4 10 28 14 1 0 57 ESE 3 7 8 8 5 1 32 SE 3 3 6 16 16 4 48 SSE 0 7 5 12 12 0 36 S 2 5 10 14 9 2 42 SSW 0 7 3 23 17 8 58 SW 1 7 9 19 11 4 51 WSW 2 18 28 38 9 7 102 W 0 12 61 52 34 34 193 WNW 1 13 38 67 37 23 179 NW 5 12 24 30 12 14 97 NNW 4 5 26 33 1 1 70 IVariable 0 0 0 0 0 0 0 Total 33 129 303 424 176 99 1164 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 3 Hours of missing stability measurements in all stability classes: 1 203 of 206

Quad Cities Nuclear Station Period of Record: October - December2005 Stability Class - Slightly Stable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total N 1 5 8 0 0 14 NNE 0 7 2 0 0 11 NE 6 7 7 7 0 27 ENE 7 9 16 1 0 33 E 5 9 4 0 1 20 ESE 2 0 2 5 1 10 SE 2 5 11 8 1 27 SSE 1 4 4 3 1 14 S 2 10 45 11 6 76 SSW 2 4 34 36 7 84 SW 1 6 22 18 2 50 WSW 0 8 9 4 0 21 W 4 13 28 3 0 49 WNW 1 20 15 2 0 38 NW 0 8 20 3 0 32 NNW 1 6 14 2 0 24 Variable 0 0 0 0 0 0 Total 11 35 121 241 103 19 530 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 5 Hours of missing stability measurements in all stability classes: 1 204 of 206

Quad Cities Nuclear Station Period of Record: October - December2005 Stability Class - Moderately Stable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_________ _ _ _ _ _ - - - - - - - - - - - - - - - - - - - - - - - - -

N 3 1 3 0 0 0 7 NNE 0 2 2 0 0 0 4 NE 1 5 5 2 0 0 13 ENE 0 6 12 2 0 0 20 E 1 4 0 1 0 0 6 ESE 0 1 3 0 0 0 4 SE 0 2 6 1 6 0 15 SSE 0 2 3 15 2 0 22 S 0 1 1 23 3 0 28 SSW 1 1 6 16 2 0 26 SW 0 5 1 0 0 0 6 WSW 0 2 5 0 0 0 7 W 0 3 0 4 3 0 10 WNW 0 0 0 7 1 0 8 NW 0 1 0 12 3 0 16 NNW 0 2 0 3 0 0 5 Variable 0 0 0 0 0 0 0 Total 6 38 47 86 20 0 197 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 8 Hours of missing stability measurements in all stability classes: 1 205 of 206

Quad Cities Nuclear Station Period of Record: October - December2005 Stability Class - Extremely Stable - 296Ft-33Ft Delta-T (F)

Winds Measured at 296 Feet Wind Speed (in mph)

Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total

_____ _____ _____

N 1 0 3 4 0 0 8 NNE 0 1 1 0 0 0 2 NE 0 0 3 3 0 0 6 ENE 0 2 1 1 0 0 4 E 1 2 0 0 0 0 3 ESE 0 1 0 0 0 0 1 SE 0 0 2 0 1 0 3 SSE 1 2 0 1 0 0 4 S 0 0 1 14 0 0 15 SSW 1 0 2 7 1 0 11 SW 1 0 1 2 1 0 5 WSW 1 4 1 0 0 0 6 W 1 3 1 1 0 0 6 WNW 0 0 0 2 0 0 2 NW 0 0 1 5 0 0 6 NNW 0 2 2 2 0 0 6 Variable 0 0 0 0 0 0 0 Total 7 17 19 42 3 0 88 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stabili ty class: 11 Hours of missing stability measurements in all sta bility cl asses: 1 206 of 206

SVP-06-048, Annual Radiological Environmental Operating Report

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MAXIMUM PERIOD DOSE TO LIMIT (I(ny Organ) ================================

MAXIMUM PERIOD DOSE TO LIMIT (Tot Body) ==========2=====================

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MAXIMUM PERIOD NG DOSE TO LIMIT (Gamma) ==============================

MAXIMUM PERIOD NG DOSE3 TO LIMIT (Beta) ==============================

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== MAXIMUM PERIOD DOSE TO LIMIT (Any Organ) =======-== == = = -==== == ----------------- =

MAXIMUM PERIOD DOSE TO LIMIT (Tot Body) ========:=========================

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