SVP-06-048, Annual Radiological Environmental Operating Report

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Annual Radiological Environmental Operating Report
ML061420402
Person / Time
Site: Quad Cities  Constellation icon.png
Issue date: 05/12/2006
From: Tulon T J
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


Text

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..........................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..........................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 TabIes Table B-1: Table B-2: Location Designation, Distance & Direction, and Sample Collection

&Analytical Methods Radiological Environmental Monitoring Program -Sampling Locations, Distance and Direction, Quad Cities Nuclear Power Station, 2005 Radiological Environmental Monitoring Program -Summary of Sample Collection and Analytical Methods, Quad Cities Nuclear Power Station, 2005 Figures Figure B-1: Figure B-2: Figure B-3: Quad Cities Outer Ring TLDs and Air Sampling Sites, 2005 Quad Cities Inner Ring TLD Locations, 2005 Quad Cities Milk, Fish, Water and Sediment Sampling Locations, 2005 Appendix C Tables Table C-1.1 Table C-1.2 Table C-1.3 Table C-11.1 Data Tables and Figures -Primary Laboratory Concentrations of Gross Beta in Surface Water Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.Concentrations of Tritium in Surface Water Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.Concentrations of Gamma Emitters in Surface Water Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.Concentrations of Tritium in Ground Water Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.ii 3 of 206 Table C-11.2 Table C-111.1 Table C-IV.1 Table C-V.1 Table C-V.2 Table C-V.3 Table C-VI.1 Table C-VII.1 Table C-VII.2 Table C-VIII.1 Table C-IX.1 Table C-IX.2 Table C-IX.3 Table C-X.1 Concentrations of Gamma Emitters in Ground Water Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.Concentrations of Gamma Emitters in Fish Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.Concentrations of Gamma Emitters in Sediment Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.Concentrations of Gross Beta in Air Particulate Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.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.Concentrations of Gamma Emitters in Air Particulate Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.Concentrations of 1-131 in Air Iodine Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.Concentrations of 1-131 in Milk Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.Concentrations of Gamma Emitters in Milk Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.Concentrations of Gamma Emitters in Food Products Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.Quarterly TLD Results for Quad Cities Nuclear Power Station, 2005.Mean Quarterly TLD Results for the Inner Ring, Outer Ring, Other and Control Locations for Quad Cities Nuclear Power Station, 2005.Summary of the Ambient Dosimetry Program for Quad Cities Nuclear Power Station, 2005.Summary of Collection Dates for Samples Collected in the Vicinity of Quad Cities Nuclear Power Station, 2005.Eigures Figure C-1 Figure C-2 Figure C-3 Figure C-4 Surface Water -Gross Beta -Stations Q-33 and Q-34 (C) Collected in the Vicinity of QCNPS, 2000 -2005.Surface Water -Tritium -Stations Q-33 and Q-34 (C) Collected in the Vicinity of QCNPS, 2000 -2005.Ground Water -Tritium -Station Q-35 and Q-36 Collected in the Vicinity of QCNPS, 2000 -2005.Air Particulates

-Gross Beta -Stations Q-01 and Q-02 Collected in the Vicinity of QCNPS, 2000 -2005.iii 4 of 206 Figure C-5 Figure C-6 Figure C-7 Figure C-8 Appendix D Air Particulates

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

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

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

-Gross Beta -Stations Q-37 and Q-38 Collected in the Vicinity of QCNPS, 2005.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 Table D-4 Table D-5 Appendix E DOE's Mixed Analyte Performance Evaluation Program (MAPEP)Teledyne Brown Engineering, 2005 ERA Statistical Summary Proficiency Testing Program Environmental, Inc., 2005 DOE's Mixed Analyte Performance Evaluation Program (MAPEP)Environmental, Inc., 2005 Errata Data Appendix F Appendix G Effluent Data 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.1 6 of 206 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.-3 -8 of 206 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-4 -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. L ower 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-5 -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. 11 of 206 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 <br />0 hours <br />0 weeks <br />0 months <br /> due to pump burn out; collector replaced pump.A/l Q-02 08/26/05 Low reading of 13.1 hours1.157407e-5 days <br />2.777778e-4 hours <br />1.653439e-6 weeks <br />3.805e-7 months <br /> 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 <br />8.333333e-4 hours <br />4.960317e-6 weeks <br />1.1415e-6 months <br /> due to replacement of malfunctioning surge protector.

A/l Q-01 10/07/05 Low timer reading of 119.4 hours4.62963e-5 days <br />0.00111 hours <br />6.613757e-6 weeks <br />1.522e-6 months <br /> 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 <br />0.00139 hours <br />8.267196e-6 weeks <br />1.9025e-6 months <br /> due to work being done at substation.

A Q-01 10/28/05 Low reading of 71.7 hours8.101852e-5 days <br />0.00194 hours <br />1.157407e-5 weeks <br />2.6635e-6 months <br /> 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.-7 -12 of 206 Table D-2 LISTING OF MISSED SAMPLES (continued)

Sample Location Type Code Collection Date Reason TLD TLD SW SW SW SW SW SW SW SW SW SW SW TLD Q-209-1 Q-209-1 Q-33 Q-34 Q-33 Q-34 Q-33 Q-34 Q-33 Q-34 Q-33 Q-34 Q-33 Quad Cities Q-01 Q-01 Q-33 Q-34 07/01/05-TLD was not changed out at the end of the 10/01/05 3rd quarter.07/01/05-TLD reading reflected 3 rd and 4 th quarter 10/01/05 combined reading.01/07/05 No sample; water frozen.01/07/05 No sample; water frozen.01/14/05 No sample; water frozen.01/14/05 No sample; water frozen.01/21/05 No sample; water frozen.01/21/05 No sample; water frozen.01/28/05 No sample; water frozen.01/28/05 No sample; water frozen.02/04/05 No sample; water frozen.02/04/05 No sample; water frozen.02/18/05 No sample; water frozen.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).10/14/05 No sample; power out; unable to field check pump.10/21/05 No sample; power out.12/09/05 No sample; water frozen.12/09/05 No sample; water frozen.A A/I SW SW-8 -13 of 206 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.-9-14 of 206 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.-10-15 of 206 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-1 1 -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-12 -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 1/2 degree 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.-14-19 of 206 Sector AN B NNE CNE D ENE E E F ESE G SE H SSE JS K SSW L SW M WSW NW P WNW Q NW R NNW Distance in Miles from QCNPS Residence Livestock Miles Miles 0.6 2.7 3.8 5.4 1.3 2.9 2.9 2.3 2.7 2.8 3.1 2.5 5.5 1.1 3.6 0.8 1.6 3.2 2.9 3.3 2.2 2.2 2.6 4.3 2.7 3.8 2.6 2.6 2.1 2.2 Milk Farm Miles 3.1 6.6 4.6 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.-15-20 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:-16-21 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.-17-22 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 (PCI/LITER)

GR-B 4 4 6.5 (1/2)5.9 (1/2)6.5 (1/2)Q-33 INDICATOR CORDOVA 3.1 MILES SSW OF SITE 0 H-3 GAMMA MN-54 CO-58 FE-59 CO-60 ZN-65 NB-95 2 4 200 <LLD<LLD 0 15 <LLD 15 <LLD 30 <LLD 15 <LLD 30 <LLD 15 <LLD<LLD 0<LLD 0<LLD 0<LLD 0<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 1-131 CS-134 CS-137 BA-140 LA-140 30 <LLD 15 <LLD 15 <LLD 18 <LLD 60 <LLD 15 <LLD<LLD 0<LLD 0<LLD 0<LLD 0<LLD 0<LLD 0 GROUND WATER (PCI/LITER)

H-3 2 200 <LLD N/A 0 GAMMA MN-54 2 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 FE-59 CO-60 ZN-65 NB-95 ZR-95 CS-134 CS-137 15 <LLD 30 <LLD 15 <LLD 30 <LLD 15 <LLD 30 <LLD 15 <LLD 18 <LLD N/A 0 N/A 0 N/A 0 N/A 0 N/A 0 N/A 0 N/A 0 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 LA- 140 60 <LLD 15 <LLD N/A N/A 0 AIR PARTICULATE (E-3 PCI/CU.METER)

GR-B 65 10 27 (52/52)(12/49)29 (13/13)(17/52)29 (13/13)(17/52)Q-07 CONTROL CLINTON 8.9 MILES NE OF SITE 0 GAMMA MN-54 5 CO-58 FE-59 CO-60 ZN-65 N/A <LLD N/A <LLD N/A <LLD N/A <LLD N/A <LLD<LLD 0<LLD 0<LLD 0<LLD 0<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 CS-137 BALA 140 10 <LLD 10 <LLD N/A <LLD<LLD<LLD 0<LLD 0> AIR IODINE ti (E-3 PCI/CU.METER)

MILK (PCI/LITER) 1-131 1-131 30 3 70 <LLD I <LLD<LLD 0 N/A 0 GAMMA MN-54 CO-58 3 N/A <LLD N/A <LLD N/A 0 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 CO-60 ZN-65 ZRNB-95 CS-134 CS-137 BA-140 LA-140 N/A <LLD N/A <LLD N/A <LLD N/A <LLD 15 <LLD 18 <LLD 60 <LLD 15 <LLD N/A 0 N/A 0 N/A 0 N/A 0 N/A 0 N/A 0 N/A 0 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 (MILLI-ROENTGEN/QTR)

TLD-QUARTERLY 78 N/A 25.2 (78/78)(22/31)N/A 31.0 (1/1)Q-203-2* INDICATOR 5.0 MILES NE OF SITE 0 CA)0 Oh t.J 0i C.* Locations Q-203-2 and Q-211-1 had identical results of 31.0 mR. Only Q-203-2 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-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 (PCI/LITER)

GR-B 6 4 5.5 (1/3)5.2 (1/3)5.5 (1/3)Q-33 INDICATOR CORDOVA 3.1 MILES SSW OF SITE 0 H-3 GAMMA MN-54 2 6 CO-58 00 200 <LLD 15 <LLD 15 <LLD 30 <LLD 15 <LLD 30 <LLD 15 <LLD<LLD 0<LLD<LLD 0 0 FE-59 CO-60 ZN-65 NB-95<LLD 0<LLD 0<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 1-13 1 CS-134 CS-137 BA-140 LA-140 30 <LLD 15 <LLD 15 <LLD 18 <LLD 60 <LLD 15 <LLD<LLD 0<LLD 0<LLD 0<LLD 0<LLD 0<LLD GROUND WATER (PCI/LITER)

H-3 2 200 <LLD N/A 0 GAMMA MN-54 15 <LLD N/A 0 0 a.h tSi C)an%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 CO-58 FE-59 CO-60 ZN-65 15 <LLD 30 <LLD 15 <LLD 30 <LLD 15 <LLD 30 <LLD 15 <LLD 18 <LLD N/A 0 N/A 0 N/A 0 N/A 0 l NB-95 N/A 0 ZR-95 CS-134 CS-137 N/A 0 N/A 0 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 LA-140 FISH (PCI/KG WET)GAMMA MN-54 4 CO-58 FE-59 CO-60 ZN-65 ZRNB-95 60 <LLD 15 <LLD 130 <LLD 130 <LLD 260 <LLD 130 <LLD 260 <LLD N/A <LLD N/A 0 N/A<LLD 0 0<LLD 0<LLD 0<LLD 0<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 CS-137 BALA140 SEDIMENT (PCI/KG)GAMMA MN-54 I t-'130 <LLD 150 <LLD N/A <LLD N/A <LLD N/A <LLD N/A <LLD N/A <LLD N/A <LLD<LLD 0<LLD 0<LLD N/A 0 0 CO-58 N/A 0 FE-59 CO-60 ZN-65 N/A 0 N/A 0 N/A LA Ln 0 to all 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 ZRNB-95 CS-134 CS-137 BALA140 N/A <LLD 150 <LLD 180 <LLD N/A <LLD N/A 0 N/A 0 N/A 0 N/A 0 I: AIR PARTICULATE (E-3 PCI/CU.METER)

GR-B 65 10 19 (52/52)(11/28)22 (12/13)(16/36)22 (12/13)(16/36)Q-07 CONTROL CLINTON 8.9 MILES NE OF SITE 0 GAMMA MN-54 5 N/A <LLD CO-58 FE-59 N/A <LLD N/A <LLD<LLD<LLD<LLD 0 0 0 W L.J 0 I-h 0bi 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 CO-60 ZN-65 ZRNB-95 CS-134 CS-137 BALA140 N/A <LLD N/A <LLD N/A <LLD 10 <LLD 10 <LLD N/A <LLD<LLD 0<LLD 0<LLD 0<LLD 0<LLD 0<LLD 0 AIR IODINE (E-3 PCI/CU.METER) 1-131 35 70 <LLD<LLD MILK (PCtILITER) 1-131 5<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 GAMMA MN-54 5 N/A <LLD N/A 0 CO-58 FE-59 CO-60 ZN-65 N/A <LLD N/A <LLD N/A <LLD N/A <LLD N/A 0 N/A 0 N/A 0 N/A 0 ZRNB-95 N/A<LLD N/A 0 CS-134 CS-137 15 <LLD 18 <LLD N/A 0 N/A 0 w 0, 0 Iti CD 0 0o 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 LA- 140 60 <LLD 15 <LLD N/A 0 N/A 0 DIRECT RADIATION (MILLI-ROENTGEN/QTR)

TLD-QUARTERLY 80 N/A 17.7 (78/78)(16/22)17.0 (2/2)(17/17)22.0 (1/1)Q-214-2* INDICATOR 4.4 MILES WNW OF SITE 0 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 (PCI/LITER)

GR-B 6 2 4 4.4 (3/3)(2.9/5.8)200 223 (1/1)4.7 (3/3)(4.2/5.3)211 (1/1)4.7 (3/3)(4.2/5.3)223 (1/1)Q-34 CONTROL CAMANCHE -UPSTREAM 4.4 MILES NNE OF SITE Q-33 INDICATOR CORDOVA 3.1 MILES SSW OF SITE 0 0 H-3 GAMMA MN-54 CO-58 FE-59 CO-60 ZN-65 NB-95 6 15 <LLD 15 <LLD 30 <LLD 15 <LLD 30 <LLD 15 <LLD<LLD 0<LLD 0<LLD 0<LLD<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 1-131 CS-134 CS-137 BA-140 LA-140 30 <LLD 15 <LLD 15 <LLD 18 <LLD 60 <LLD 15 <LLD 200 <LLD<LLD 0<LLD 0<LLD 0<LLD 0 00<LLD 0<LLD 0 GROUND WATER (PCI/LITER)

H-3 2 N/A GAMMA MN-54 2 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 FE-59 CO-60 ZN-65 NB-95 ZR-95 CS-134 CS-137 15 <LLD 30 <LLD 15 <LLD 30 <LLD 15 <LLD 30 <LLD 15 <LLD 18 <LLD N/A 0 N/A 0 N/A 0 N/A 0 N/A 0 N/A 0 N/A 0 N/A 0 db.3 0 Ih an 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 BA-140 LA-140 60 <LLD 15 <LLD N/A 0 N/A 0 AIR PARTICULATE (E-3 PCI/CU.METER)

GR-B 116 10 22 (101/103)(7/48)22 (13/13)(11/41)24 (13/13)(10/48)Q-13 INDICATOR PRINCETON 4.7 MILES SW OF SITE 0 GAMMA MN-54 9 k)0~CO-58 FE-59 CO-60 ZN-65 N/A <LLD N/A <LLD N/A <LLD N/A <LLD N/A <LLD<LLD<LLD 0 0<LLD 0<LLD 0<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 CS-134 CS-137 BALA140 N/A <LLD 10 <LLD 10 <LLD N/A <LLD<LLD 0<LLD<LLD 0<LLD 0> AIR IODINE S! (E-3 PCI/CU.METER) 1-131 63 70 <LLD<LLD 0 MILK (PCI/LITER) 1-131 7<LLD N/A 0 GAMMA MN-54 CO-58 7 N/A <LLD N/A <LLD N/A N/A 0 0 o th 05 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 FE-59 CO-60 ZN-65 ZRNB-95 CS-134 CS-137 BA-140 LA-140 N/A <LLD N/A <LLD N/A <LLD N/A <LLD 15 <LLD 18 <LLD 60 <LLD 15 <LLD N/A 0 N/A 0 N/A 0 N/A 0 N/A N/A 0 N/A 0 N/A 0 a, 0 bi 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 FOOD PRODUCTS (PCI/KG WET)GAMMA MN-54 10 N/A <LLD<LLD 0 CO-58 FE-59 CO-60 ZN-65 ZRNB-95 1-131 CS-134 N/A <LLD N/A <LLD N/A <LLD N/A <LLD N/A <LLD 60 <LLD 60 <LLD<LLD 0<LLD 0<LLD 0<LLD 0<LLD 0<LLD 0<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 (MILLI-ROENTGEN/QTR)

TLD-QUARTERLY 79 N/A 19.6 (77/77)(16/26)18.0 (2/2)(18/18)26.0 (1/1)Q-211-2 INDICATOR 4.5 MILES SW OF SITE 0 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 (PCI/LITER)

GR-B 6 4 5.3 (3/3)(4.7/5.8)5.7 (3/3)(5.1/6)5.7 (3/3)(5.1/6)Q-34 CONTROL CAMANCHE -UPSTREAM 4.4 MILES NNE OF SITE 0 H-3 2 GAMMA MN-54 CO-58 I'.):>t 200 <LLD 15 <LLD 15 <LLD 30 <LLD 15 <LLD 30 <LLD 15 <LLD<LLD<LLD 0<LLD 0 0 FE-59 CO-60 ZN-65 NB-95<LLD<LLD 0<LLD 0<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 1-131 CS-134 CS-137 BA-140 LA-140 30 <LLD 15 <LLD 15 <LLD 18 <LLD 60 <LLD 15 <LLD 200 <LLD<LLD 0<LLD 0<LLD 0<LLD 0 1~j<LLD 0<LLD 0 GROUND WATER (PCI/LITER)

H-3 N/A 0 GAMMA MN-54 2 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 FE-59 CO-60 ZN-65 15 <LLD 30 <LLD 15 <LLD 30 <LLD 15 <LLD 30 <LLD 15 <LLD 18 <LLD N/A 0 N/A 0 N/A 0 N/A 0 I\)NB-95 N/A 0 ZR-95 CS-134 CS-137 N/A 0 N/A 0 N/A 0 ai a%1 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 LA-140 FISH (PCI/KG WET)GAMMA MN-54 4 CO-58 FE-59 CO-60 ZN-65 ZRNB-95 60 <LLD 15 <LLD 130 <LLD 130 <LLD 260 <LLD 130 <LLD 260 <LLD N/A <LLD N/A N/A 0<LLD 0 0<LLD 0<LLD<LLD<LLD 0 0 0<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 CS-137 BALA140 130 <LLD 150 <LLD N/A <LLD N/A <LLD<LLD 0<LLD 0<LLD 0 SEDIMENT (PCI/KG DRY)GAMMA MN-54 I N/A 0 I', io CO-58 FE-59 CO-60 ZN-65 N/A <LLD N/A <LLD N/A <LLD N/A <LLD N/A 0 N/A 0 N/A 0 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 CS-134 N/A <LLD 150 <LLD N/A 0 N/A 0 CS-137 BALA140 180 90 (1/l)N/A <LLD N/A 90 (1/1)Q-39 INDICATOR 0 CORDOVA -DOWNSTREAM MISSISSIPPI RIVER 0.8 MILES SSW OF SITE N/A 0 0 tw co AIR PARTICULATE (E-3 PCIICU.METER)

GR-B 115 10 24 (102/102)(10/56)25 (13/13)(11/57)26 (13/13)(13/56)Q-13 INDICATOR PRINCETON 4.7 MILES SW OF SITE 0 GAMMA MN-54 9 N/A <LLD CO-58 FE-59 N/A <LLD N/A <LLD<LLD<LLD<LLD 0 0 0 0 t-h Isj 0)a.'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-60 ZN-65 ZRNB-95 CS-134 CS-137 BALA140 N/A <LLD N/A <LLD N/A <LLD 10 <LLD 10 <LLD N/A <LLD 70 <LLD I <LLD 0<LLD 0<LLD 0<LLD 0<LLD 0<LLD 0 AIR IODINE (E-3 PCI/CU.METER) 1-131 53 4<LLD 0 MILK (PCI/LITER) 1-131 N/A 0 To toh N)C)0A MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)

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 MN-54 4 N/A <LLD N/A 0 CO-58 FE-59 CO-60 ZN-65 ZRNB-95 CS-134 CS-137 N/A <LLD N/A <LLD N/A <LLD N/A <LLD N/A <LLD 15 <LLD 18 <LLD N/A 0 N/A 0 N/A 0 N/A 0 N/A N/A 0 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 (MILLI-ROENTGEN/QTR)

TLD-QUARTERLY 80 N/A 24.8 (78/78)(21/43*)24.5 (2/2)(24/25)43.0 (1/1)Q-209-1 INDICATOR 4.7 MILES S OF SITE 0 On 0 oh Tol 05^ TLD WAS IN SERVICE JULY THROUGH DECEMBER 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 SURFACE WATER (PCI/LITER)

GR-B 22 8 4 5.1 (8/11)(2.9/6.5)200 223 (1/4)5.3 (8/11)(4.2/6)211 (1/4)5.3 (8/11)(4.2/6)223 (1/4)Q-34 CONTROL CAMANCHE -UPSTREAM 4.4 MILES NNE OF SITE Q-33 INDICATOR CORDOVA 3.1 MILES SSW OF SITE 0 H-3 0 GAMMA 22 MN-54 15 <LLD CO-58 15 <LLD FE-59 30 <LLD CO-60 15 <LLD ZN-65 30 <LLD NB-95 15 <LLD MEAN AND RANGE BASED ON DETECTABLE MEASUREMENTS ONLY (M)<LLD 0<LLD 0<LLD<LLD 0<LLD 0<LLD 0 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 1-131 CS-134 CS-137 BA-140 LA-140 30 <LLD 15 <LLD 15 <LLD 18 <LLD 60 <LLD 15 <LLD<LLD 0<LLD 0<LLD 0<LLD 0<LLD<LLD 0 GROUND WATER (PCI/LITER)

H-3 8 200 <LLD N/A 0 GAMMA MN-54 8 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 FE-59 CO-60 ZN-65 NB-95 ZR-95 CS- 134 CS-137 15 <LLD 30 <LLD 15 <LLD 30 <LLD 15 <LLD 30 <LLD 15 <LLD 18 <LLD N/A 0 N/A 0 N/A 0 N/A 0 N/A 0 N/A 0 N/A 0 N/A Ln 0 0 0-h a, 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 0 LA- 140 FISH (PCI/KG WET)GAMMA MN-54 8 CO-58 FE-59 CO-60 ZN-65 ZRNB-95 15 <LLD 130 <LLD 130 <LLD 260 <LLD 130 <LLD 260 <LLD N/A <LLD N/A<LLD 0<LLD 0 0<LLD 0<LLD 0<LLD<LLD 0 0 0o 0 Ha.Tol 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 CS-134 CS-137 BALA140 130 <LLD 150 <LLD N/A <LLD N/A <LLD<LLD 0<LLD 0<LLD 0 SEDIMENT (PCI/KG DRY)GAMMA MN-54 2 N/A 0 00 CO-58 FE-59 CO-60 ZN-65 N/A <LLD N/A <LLD N/A <LLD N/A <LLD N/A N/A N/A N/A 0 0 0 0 0 as ti oh)CY)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 ZRNB-95 N/A <LLD N/A 0 CS-134 150 <LLD N/A 0 CS-137 BALA 140 180 90 (1/2)N/A <LLD N/A N/A 90 (1/2)Q-39 INDICATOR 0 CORDOVA -DOWNSTREAM MISSISSIPPI RIVER 0.8 MILES SSW OF SITE 0 AIR PARTICULATE (E-3 PCI/CU.METER)

GR-B 361 10 23 (307/309)(7/56)24 (51/52)(11/57)25 (26/26)(10/56)Q-1 3 INDICATOR PRINCETON 4.7 MILES SW OF SITE 0 GAMMA MN-54 28 N/A <LLD CO-58 FE-59 N/A <LLD N/A <LLD<LLD<LLD<LLD 0 0 01%0 1-h 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 CO-60 ZN-65 ZRNB-95 CS-134 CS-137 BALA140 N/A <LLD N/A <LLD N/A <LLD 10 <LLD 10 <LLD N/A <LLD 70 <LLD<LLD 0<LLD 0<LLD 0<LLD 0 4<LLD 0<LLD 0 AIR IODINE (E-3 PCI/CU.METER) 1-131 181<LLD 0 MILK (PCI/LITER) 1-131 19 I <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 GAMMA MN-54 CO-58 FE-59 CO-60 ZN-65 ZRNB-95 CS-134 CS-137 19 N/A <LLD N/A <LLD N/A <LLD N/A <LLD N/A <LLD N/A <LLD 15 <LLD 18 <LLD N/A 0 N/A 0 N/A 0 N/A 0 N/A 0 N/A 0 N/A 0 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 (PCI/KG WET)GAMMA MN-54 10 N/A <LLD<LLD CO-58 FE-59 CO-60 ZN-65 ZRNB-95 N/A <LLD N/A <LLD N/A <LLD N/A <LLD N/A <LLD<LLD 0<LLD 0<LLD 0<LLD 0<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 CS-137 BALA140 60 <LLD 80 <LLD N/A <LLD<LLD 0<LLD 0<LLD 0 DIRECT RADIATION (MILLI-ROENTGEN/QTR)

TLD-QUARTERLY 317 N/A 24.8 (311/31 1)(16/43*)19.8 (6/6)(17/25)430 (3/4)(18/43*)Q-209-1 INDICATOR 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 0-34 Cordova (indicator)

Camanche, Upstream (control)3.1 miles SSW 4.4 miles NNE B Gmrund/WpIl Water Q-35 Q-36 McMillan Well (indicator)

Cordova Well (indicator)

1.5 miles

S 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 Q-02 Q-03 Q-04 Q-07 Q-13 Q-16 Q-37 Q-38 Onsite 1 (indicator)

Onsite 2 (indicator)

Onsite 3 (indicator)

Nitrin (indicator)

Clinton (control)Princeton (indicator)

Low Moor (indicator)

Meredosia Road (indicator)

Fuller Road (indicator)

Pool #14 of Mississippi River, Downstream (indicator)

Mississippi River, Upstream (control)0.5 miles N 0.4 miles ENE 0.6 miles S 1.7 miles NE 8.9 miles NE 4.7 miles SW 5.7 miles NNW 4.4 miles ENE 4.7 miles E 0.5 miles SW 1.0 miles N F Fish Q-24 Q-29 F. Sedinment Q-39 Cordova, Downstream on Mississippi River (indicator)

0.8 miles

SSW fi Frd Prmdi uitrt Quadrant 1 Quadrant 2 Quadrant 3 Quadrant 4 Control Janet Price Dale Nimmic Amy Johnston Mike Fawcett Charles Leavens 6.0 miles NE 3.0 miles ESE 1.8 miles S 4.5 miles NW 9.5 miles NE , gAA __,_. T n I-i .-n~mnpnr, I;ogmeIry

-I I I~nnLerRun 0-101-1 Q-101-2 Q-102-1 0-102-3 Q-103-1 and -2 Q-104-1 0-104-2 Q-105-1 and -2 Q-106-2 and -3 0-107-2 Q-107-3 0-108-1 Q-108-2 0.6 miles N 0.9 miles N 1.3 miles NNE 1.4 miles NNE 1.2 miles NE 1.1 miles ENE 0.9 miles ENE 0.8 miles E 0.7 miles ESE 0.7 miles SE 0.8 miles SE 1.0 miles SSE 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 Q-109-2 0-111-1 Q-111-2 Q-112-1 0-112-2 Q-113-1 and-2 Q-114-1 Q-114-2 Q-115-1 0-115-2 Q-116-1 Q-116-3 0.9 miles S 1.2 miles S 2.6 miles SW 2.5 miles SW 2.5 miles WSW 2.2 miles WSW 2.5 miles W 2.1 miles WNW 2.5 miles WNW 2.6 miles NW 2.3 miles NW 2.3 miles NNW 2.4 miles NNW Ou iar Ring Q-201-1 and -2 Q-202-1 0-202-2 Q-203-1 Q-203-2 0-204-1 Q-204-2 Q-205-1 Q-205-4 Q-206-1 and -2 Q-207-1 and -4 Q-208-1 Q-208-2 Q-209-1 and -4 Q-210-1 and -4 Q-211-1 and-2 0-212-1 Q-212-2 Q-213-1 Q-213-2 Q-214-1 Q-214-2 Q-215-1 Q-215-2 Q-216-1 Q-216-2 4.2 miles N 4.4 miles NNE 4.8 miles NNE 4.7 miles NE 5.0 miles NE 4.7 miles ENE 4.5 miles ENE 4.7 miles E 4.8 miles E 4.8 miles ESE 4.7 miles SE 4.3 miles SSE 4.9 miles SSE 4.7 miles S 4.1 miles SSW 4.5 miles SW 5.4 miles WSW 4.4 miles WSW 4.3 miles W 4.8 miles W 4.7 miles WNW 4.4 miles WNW 5.0 miles NW 4.2 miles NW 4.6 miles NNW 4.3 miles NNW Q-01 Q-02 Q-03 Q-04 Q-13 Q-16 Q-37 Q-38 Onsite I (indicator)

Onsite 2 (indicator)

Onsite 3 (indicator)

Nitrin (indicator)

Princeton (indicator)

Low Moor (indicator)

Meredosia Road (indicator)

Fuller Road (indicator)

0.5 miles

N 0.4 miles ENE 0.6 miles S 1.7 miles NE 4.7 miles SW 5.7 miles NNW 4.4 miles ENE 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 in water (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 in charcoal 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 1t141 2441 a, a 2644 0 am EL m -1 a 21043 OF 204&11 2004 a *7 S 2*7-4* uXmp0Jlngss

  • a ouM sa" LO Aitr Samplimn Sites 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 IPm 014 4o Mhppi Mv 444 UV, Ca k (C)Q4-2 am Staa DriS Mc6etin W w isppi Rhr. Uptwn Q-36 Qa ba WOl Q4 Co*w 4 F39 C1*v r*tftm u S W o~r Figure B-3 Quad Cities Milk, Fish, Water and Sediment Sampling Locations, 2005 B-7 74 of 206 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 FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC (1)< 4.0 (1)6.5 +/- 1.3 5.5 +/- 1.1< 4.0< 4.0 2.9 +/- 1.8 4.6 +/- 1.8 5.8 +/- 1.9 4.7 +/- 1.7 5.2 +/- 1.8 5.8 +/- 2.0 (1)5.9 +/- 1.2 (1)< 4.0 5.2 +/- 1.2< 4.0< 4.0 4.7 +/- 2.0 5.3 +/- 1.9 4.2 +/- 1.8 6.0 +/- 1.8 5.9 +/- 1.8 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 JAN-MAR APR-JUN JUL-SEP OCT-DEC< 200< 200 22:< 166 Q-33 Q-34< 200< 200 3 +/- 112 211 +/- 113< 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 0 STC COLLECTION PERIOD Q-33 JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC Q-34 JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC MN-54< 15< 15< 15< 15< 15< 1< 2< 6<5<4< 2< 15< 15< 15< 15< 15<1< 1< 4< 3< 5< 3 (1)(1)< 15< 15< 15< 15< 15<1<2<5< 4<4< 2< 15< 15< 15< 15< 15< 1<2< 5< 4< 5< 4< 30< 30< 30< 30< 30<3< 5< 14< 9< 11<6< 30< 30< 30< 30< 30< 3<4< 6< 8< 11< 8< 15< 15< 15< 15< 15< 1< 2<5<4< 5<4< 15< 15< 15< 15< 15< 1<1<4<4<4< 3< 30< 30< 30< 30< 30< 2< 4< 10< 8< 8< 5< 30< 30< 30< 30< 30< 2< 3< 10< 7< 9< 7< 15< 15< 15< 15< 15< 1< 2< 7< 6< 5< 3< 15< 15< 15< 15< 15< 1< 2< 4< 4< 6< 4< 30< 30< 30< 30< 30< 2< 4< 9< 9< 8< 5< 30< 30< 30< 30< 30< 2< 3< 9<8< 9<7< 15< 15< 15< 15< 15<3< 14< 14< 14< 12<7< 15< 15< 15< 15< 15<3< 11< 10< 12< 13< 10< 15< 15< 15< 15< 15< 1<2<6<4<4<2< 18< 18< 18< 18< 18< 1<2<7<5<5<3<60<60<60<60<60<39< 21<31<32<28< 16<15<15<15< 15< 15<12<7<12< 9< 12<5 CO-58 FE-59 CO-60 ZN-65 NB-95 ZR-95 1-131 CS-134 CS-137 BA-140 LA-140< 15< 15< 15< 15< 15< 1< 1<4<3<5<3< 18< 18< 18<18< 18< 1< 1<5<3<5<3<60<60< 60<60<60<42< 17< 25<26< 33< 23<15<15<15< 15< 15<14<5< 9< 9< 10<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 JAN-MAR APR-JUN JUL-SEP OCT-DEC 0-35 0-36< 200< 200< 175' 186< 200< 200< 176< 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 Q-35 JAN APR JUL OCT Q-36 JAN APR JUL OCT m MN-54< 15< 15< 6<4< 15< 15< 7< 6 CO-58< 15< 15< 7< 3< 15< 15< 9< 5 FE-59< 30< 30< 11< 11< 30< 30< 20< 13 CO-60< 15< 15< 6< 3< 15< 15< 7<6 ZN-65< 30< 30< 11< 6< 30< 30< 18< 10 NB-95< 15< 15<6< 5< 15< 15< 9< 6 ZR-95< 30< 30< 11< 8< 30< 30< 16< 11 CS-134< 15< 15< 5< 4< 15< 15< 6< 6 CS-1 37 BA-140< 18 <60< 18 < 60<7 <35<4 <27 LA-140< 15< 15< 10< 9< 15< 15< 8< 10-< 18< 18< 8< 6< 60< 60< 43< 31 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 PERIOD MN-54 CO-58 FE-59 CO-60 ZN-65 ZRNB-95 CS-134 CS-137 BALA-140 STC Q-24 Golden Redhorse Channel Catfish Largemouth Bass Channel Catfish Q-29 Walleye River Carpsucker Common Carp Channel Catfish 05/18/05 05/18/05 10/11/05 10/11/05 05/18/05 05/18/05 10/11/05 10/11/05< 130< 130< 84< 54< 130< 130< 62< 52< 130< 130< 91< 53< 130< 130< 38< 67< 260< 260< 196< 132< 260< 260< 131< 128< 130< 130< 57< 57< 130< 130< 48< 67< 260< 260< 170< 106< 260< 260< 100< 140< 200< 200< 94< 49< 200< 200< 48< 70< 100< 100< 75< 61< 100< 100< 44< 58< 100< 100< 82< 58< 100< 100< 55< 57< 300< 300< 115< 161< 300< 300< 91< 150 en 00 0 Oh 0)DUE TO VENDOR CHANGE, < VALUES ARE LLD VALUES JANUARY THROUGH JUNE AND MDC VALUES JULY THROUGH DECEMBER TABLE C4V.1 CONCENTRATIONS OF GAMMA EMITTERS IN SEDIMENT SAMPLES COLLECTED IN THE VICINITY OF QUAD CITIES NUCLEAR POWER STATION, 2005 RESULTS IN UNITS OF PCI/KG DRY i 2 SIGMA STC COLLECTION PERIOD MN-54 CO-58 FE-59 CO-60 ZN-65 ZRNB-95 CS-134 CS-137 BALA-140_ A _ AA PA _ _ ~~~~- _A_--A A AAA AA_._AsA Q-39 05120105 10/06/05< 150< 77< 100< 76< 600< 165< 100< 84< 600< 176< 200< 91< 150< 68< 180 < 600 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 A ._ A AX A .WEEK 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 Q-01 32 +/- 4 47

  • 4 37 +/- 4 22+/- 4 28 i 4 26 +/- 4 26 +/- 4 31 +/- 3 24 +/- 5 21 +/- 4 18 t 3 12 +/- 3 22 +/- 3 19 +/- 3 19 +/- 4 23 +/- 3 15 +/- 3 25 +/- 4 19 +/- 4 14 +/- 3 18 +/- 4 17 +/- 3 18 +/- 3 13 +/- 4 23 +/- 3 26 i 3 7 25 +/- 5 19 +/- 5 13 +/- 5 23 +/- 5 26 +/- 5 22 +/- 5 9 +/- 4 22 +/- 4 29 +/- 5 36 +/- 5 31 +/- 5 14 +/- 4 26 +/- 6 (2)(2)17 +/- 7 27 +/- 5 28 +/- 5 12 +/- 4 17 +/- 4 15 +/- 4 32 +/- 5 27 +/- 5 50 +/- 6 33 +/- 5 w Q-02 35 +/- 4 39 +/- 4 39 +/- 4 20 +/- 4 27 +/- 4 24 +/- 3 25 +/- 4 29 +/- 3 17 +/- 4 25 +/- 4 20 +/- 3 13 +/- 3 22 +/- 3 18 +/- 3 25 +/- 4 24 +/- 3 15 +/- 3 23 +/- 4 19 +/- 4 13 +/- 3 16 +/- 3 17 +/- 3 18 +/- 3 12 +/- 4 22 +/- 3 19 +/- 3 7 5 19 +/-5 14 +/- 5 14 +/- 5 30 +/- 6 21 +/- 5 16 +/- 5 (2)30 +/- 6 26 : 5 29 +/- 5 31 +/- 5 18 +/- 4 15 +/-t4 13 +/-4 16 +/- 4 16 +/-4 24 +/- 5 27 +/- 5 17 +/- 4 15 +/-4 17 +/- 4 30 +/- 5 26 +/- 5 50+/- 6 30 +/- 5 Q-U3 43 +/- 5 47 +/- 4 48 +/- 5 25 +/- 4 28 +/- 4 24 +/- 3 26 +/- 4 32 +/- 3 22 +/- 4 21 +/- 4 18 +/- 3 14 +/- 3 25 +/- 3 21 +/- 4 22 +/- 4 28 +/- 4 17 +/- 3 24 +/- 4 19 +/- 4 15 +/- 3 17 +/- 3 18 +/- 4 19 +/- 3 14 +/- 4 24 +/- 3 28 +/-A3 11+/- 5 25 5 22 5 14+/- 4 28+/- 5 25+/- 5 20 5 13 +/-5 22. 4 27 5 41 5 31+/- 5 19 4 14 +/- 4 11 i4 19 4 11 +/-3 33 +/- 5 31 +/- 5 14 +/- 4 12 I 4 16 +/-4 30 +/- 5 25 +/- 5 46 +/- 6 33+/-5-U-04 40 5 49+/- 4 40. 4 27 4 26+/- 4 22+/- 3 28 +/- 4 33 +/- 3 16+/- 4 22. 4 20 +/-,3 16 +/-A3 24 3 20+/- 4 23 +/-A4 22 +/-A3 17+/- 3 25 +/- 4 18 +/- 4 18 +/- 3 15 +/- 3 17 3 15 3 11 +/-4 24+/- 3 26 +/-A3 11 5 19 5 12 5 15+/- 5 25+/- 5 23+/- 5 15 ,5 11 +/-5 27. 5 31+/- 5 24 4 30+/- 5 15 +/-4 12 +/-4 t17 4 16 4 15+/-4 32 5 36+/- 5 14 +/-4 14 +/- 4 18 +/- 4 34 +/-5 23 +/- 5 55 +/- 6 34A.5 GROUP 11 Q-13 Q-16 Q-37 (1) (1) (1)l GROUP III Q-38 Q-07 (1) 38+/-5 52 +/- 4 43 +/- 5 29 +/- 4 28 +/- 4 23 +/- 3 28 +/- 4 33 +/- 3 17 +/- 4 24 +/- 5 19 +/- 3 17 +/- 3 28 +/- 4 20 +/- 3 21 +/- 4 28 +/- 3 18 +/- 3 27 +/- 4 22 +/- 4 17 +/- 3 16 +/- 3 17 +/- 4< 10 18 +/- 3 24 +/- 3 36 +/- 4 8+/-5 11+/-4 19+/-5 25 5 21+/-5 18+/-5 13 5 12+/-4 28 5 30+/-6 26+/-5 22+/-5 16+/-5 16 5 6 12+/-5 28+/-5 21+/-4 37+/-5 34+5 44A+/-6 41+/-5 34A+/-5 28+/-5 16 +/-4 17 +/-,4 16 +/- 4 15 +/- 4 18 +/-4 19+/-.4 22A+/-4 18 +/- 4 13 +/-,3 18+/-4 25 +/-5 25+/-5 24A+/-5 37A+/-5 10 +/-4 17 +/-4 15 +/-4 11 4 16+/-4 17+/-4 29 +/-5 30+/-5 23A+/-5 25+/-5 55A+/-6 57+/-6 30^+/-5 32 5 I 10 +/-4 27 +/- 5 18 +/- 5 12 +/- 4 28 +/- 6 23 +/- 5 21 +/- 5 16 +/- 5 29 +/- 5 32 +/- 5 48A+/-6 35 +/- 5 19 +/-4 13 +/- 4 19 +/- 5 18 +/-4 17 +/- 4 28 +/- 5 36 +/- 5 14 +/-4 16 t 4 22 +/- 4 40 +/- 6 29 +/- 5 56 +/- 6 36A+/-5 11 +/-4 24 +/- 5 16 +/- 5 11 +/-4 25 +/- 5 25 +/- 5 18 +/-5 11 +/-4 24 +/- 5 31 +/-5 41 +/- 5 30 +/- 5 14 +/-,4 14 +/-4 21 i 5 19 +/-,4 17 +/-A4 26 +/- 5 33 +/- 5 16 +/- 4 13 +/-4 18 +/-A4 36 +/- 5 29 +/- 5 53 +/- 6 38 +/- 5 11 +/- 5 24 +/- 5 18 +/- 5 11 +/-4 28 +/- 5 21 +/- 5 22 +/- 5 11 +/-5 22 +/- 4 24 +/- 5 41 +/- 5 30 i 5 14 +/- 4 14 +/-4 17 +/-4 19 i 4 17 +/- 4 30 i 5 32 +/- 5 14 i 4 13 +/-4 15 4 4 32 +/- 5 25 +/- 5 55 +/- 6 38 +/- 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) IN AIR 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 -CONTF 12 O0 03/04/04/06, 07/071 O9R 09/11/12/COLLECTION MIN. MAX. MEAN +/-PERIOD 2 SD 131/04 -01/28/05 20 49 37 +/- 19/28/05 -02/26/05 22 33 27 +/- 6 ,04/05 -04/02/05 12 25 20 +/- 8.08/05 -04/29/05 15 28 21 +/- 8.29/05 -06/03/05 13 25 18 +/- 7 i04/05 -07/02/05 11 28 20 11'02/05 -07/29/05 < 7 25 16 11'29/05 -09/02/05 9 30 21 +/- 12 f02/05 -09/30/05 14 41 27 +/- 15'30/05 -11/03/05 11 26 15 i 8'03/05 -12/02/05 12 36 19 +/- 15'02/05 -12/30/05 23 55 35 +/- 19 COLLECTION PERIOD 12/31/04 -01/28/05 01/28/05 -02/26/05 03/04/05 -04/02/05 04/08/05 -04/29/05 04/29/05 -06/03/05 06/04/05 -07/02/05 07/02/05 -07/29/05 07/29/05 -09/02/05 09/02/05 -09/30/05 09/30/05 -11/03/05 11/03/05 -12/02/05 12/02/05 -12/30/05 MIN. MAX. MEAN +/-2 SD (1) (1) (1)8 27 16 +/- 12 6 29 21+/- 13 14 48 31+/- 21 13 28 18 +/- 8 10 36 19+/- 16 23 56 38+/- 22.I COLLECTION PERIOD 12/31/04 -01/28/05 01/28/05 -02/26/05 03/04/05 -04/02/05 04/08/05 -04/29/05 04/29/05 -06/03/05 06/04/05 -07/02/05 07/02/05 -07/29/05 07/29/05 -09/02/05 09/02/05 -09/30/05 09/30/05 -11/03/05 11/03/05 -12/02/05 12/02/05 -12/30/05 IOL LOCATIONS MIN. MAX. MEAN +/-2 SD 29 52 41 +/- 19 23 33 28 +/- 8 17 28 22 +/- 10 18 28 22 +/- 10 16 27 20 +/- 9 8 36 22 +/- 23 11 25 17 +/- 13 12 30 20 +/- 13 17 41 30 +/- 21 15 25 19 +/- 7 11 37 20 +/- 23 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 0 O-h 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 PERIODl MN-54 C0-58 FE-59 C0-60 ZN-65 ZRNB-95 CS-134 CS-137 BALA140 Q-01 12/31/04 04/02/05 04/02/05 07/02/05 07/02/05 09/30/05 09/30/05 12/30/05 Q-02 12/31/04 04/02/05 04/02105 07/02/05 07/02/05 09/30/05 09/30/05 12/30/05< 10.0< 10.0<4.2< 2.8< 10.0< 10.0< 2.8< 3.0< 10.0< 10.0< 3.9< 2.2< 10.0< 10.0< 3.1< 2.2< 15.0< 15.0< 18< 4.9< 15.0< 15.0< 5.0< 6.9< 10.0< 10.0< 1.9< 6.4< 10.0< 10.0< 3.6< 2.4< 40.0< 40.0< 13< 8.4< 40.0< 40.0< 4.9< 5.4< 10.0< 10.0< 6.4< 2.8< 10.0< 10.0< 4.3< 2.8< 10.0< 10.0< 4.7< 2.4< 10.0< 10.0< 2.2< 2.6< 1u.u< 10.0< 4.1< 3.0< 10.0< 10.0< 1.7< 2.5< MM.< 25.0< 87< 9.3< 25.0< 25.0< 79< 13 D C-)Q-03 12131/04 04/02/05 04/02105 07/02/05 07/02/05 09/30/05 09/30/05 12130/05 Q-04 12/31/04 04/02105 04/02/05 07/02/05 07/02/05 09/30/05 09/30/05 12/30/05 Q-07 12/31/04 04/02/05 04/02/05 07/02/05 07/02/05 09/30/05 09/30/05 12/30/05< 10.0< 10.0< 2.1< 2.3< 10.0< 10.0< 2.7< 2.8< 10.0< 10.0< 3.2< 2.8< 10.0< 10.0< 2.4< 2.7< 10.0< 10.0< 2.1< 2.8< 10.0< 10.0< 3.5< 2.9< 15.0< 15.0< 8.8< 3.7< 15.0< 15.0< 7.1< 6.0< 15.0< 15.0< 8.6< 6.4< 10.0< 10.0< 1.8< 2.5< 10.0< 10.0< 1.5< 1.0< 10.0< 10.0< 2.9< 2.4< 40.0< 40.0< 5.4< 5.6< 40.0< 40.0< 6.0< 7.3< 40.0< 40.0< 6.7< 5.9< 10.0< 10.0< 2.7< 2.9< 10.0< 10.0< 4.5< 2.5< 10.0< 10.0< 5.2< 2.4< 10.0< 10.0< 2.0< 2.3< 10.0< 10.0< 1.3< 2.5< 10.0< 10.0< 2.8< 3.1< 10.0< 10.0< 1.7< 1.9< 10.0< 10.0< 2.0< 2.2< 10.0< 10.0< 3.2< 2.7< 25.0< 25.0< 40< 10< 25.0< 25.0< 69< 12< 25.0< 25.0< 31< 16 DUE TO VENDOR CHANGE, THROUGH DECEMBER<VALUES ARE LLD VALUES JANUARY THROUGH JUNE AND MDC VALUES JULY 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 PERIOD MN-54 CO-58 FE-59 CO-60 ZN-65 ZRNB-95 CS-134 CS-137 BALA140 I Q-13 (1)(1)07/02/05 09/30/05 09/30/05 12/30/05<4.3< 2.7< 6.1<3.2< 19< 6.8< 4.1< 3.0< 9.5< 8.8< 6.7< 3.1< 4.4< 3.4< 4.2< 3.3< 91< 7.6 C)Q-16 0-37 Q-38 (1)(1)07/02/05 09/30/05 09/30/05 12/30/05 (1)(1)07/02/05 09/30/05 09/30/05 12/30/05 (1)(1)07/02/05 09/30/05 09/30/05 12/30/05< 3.3< 2.8< 2.4< 2.4< 1.9< 2.3< 4.7< 3.0< 4.2< 2.1< 3.8< 2.7< 14< 7.7< 2.9< 3.3< 11< 6.6< 3.3< 2.5< 3.0< 2.9< 3.6< 3.0< 11< 5.6< 7.4< 3.6< 6.8< 4.8< 5.4< 3.1< 2.8< 2.5< 5.1< 2.7< 4.9< 3.1< 1.7< 1.9< 2.1< 2.2< 3.9< 2.8< 2.4< 2.3< 1.5< 2.2< 45< 15< 69< 12< 17< 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 IN AIR 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 PERIOD 01/07/05 02/04/05 03/04/05 04/02/05 05/06/05 05/20/05 06/03/05 06/17/05 07/02/05 07115/05 07/29/05 08/12/05 08/26/05 09/09/05 09/23/05 10/07/05 10/21/05 11/04/05 12/02/05 INDICATOR FARM Q-26< 1.0< 1.0< 1.0< 1.0< 1.0< 1.0< 1.0< 1.0< 1.0< 0.6< 0.9< 0.4< 0.3< 0.7< 0.5< 0.7< 0.9< 0.6< 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 PERIOD Q-26 01/07/05 02/04/05 03/04/05 04/02/05 05/06/05 05/20/05 06/03/05 06/17/05 07/02/05 07/15/05 07/29/05 08/12/05 C) 08/26/05 09109/05 09/23/05 10/07/05 10/21/05 11/04/05 12/02/05 MN-54 CO-58 FE-59 CO-60 ZN-65 ZRNB-95 CS-134 CS-137 BA-140 LA-140' 10< 10< 10' 10< 10< 10< 10< 10' 10< 7< 6< 4<5< 6< 7<6< 6< 5< 2< 10< 10< 10< 10' 10< 10< 10< 10< 10<9< 5<4<6< 7<7<4< 6<5< 2< 15< 15< 15< 15< 15< 15< 15< 15< 15< 17< 17< 11< 12< 14< 18< 12< 13< 16< 5< 10< 10< 10< 10< 10< 10< 10< 10< 10< 16< 6< 4< 4< 8< 7< 7< 6< 6<2' 15< 15< 15< 15< 15< 15< 15' 15< 15< 18< 17< 14< 7< 15< 16< 10< 12< 14< 5< 10< 10< 10< 10< 10' 10< 10< 10< 10< 7<7< 5< 6< 7< 8< 6< 6< 6< 2< 15< 15< 15< 15< 15< 15< 15' 15< 15<6< 7< 4< 4< 6< 7< 4< 5< 5<2< 18< 18< 18< 18< 18< 18< 18< 18< 18< 8< 5< 5< 5< 6< 8< 5< 6< 7< 2< 60< 60< 60< 60< 60< 60< 60< 60< 60< 39< 38< 21< 27< 38< 41< 24< 31< 32<9< 15< 15< 15< 15< 15< 15< 15< 15< 15< 14<9< 6<9< 12< 12< 8<9< 11< 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 PERIOD CO-s8 FE-59 0-QUAD Rhubarb Leaves 0-QUAD 1 Onions 0-QUAD 2 Rhubarb Leaves 0-QUAD 2 Onions 0-QUAD 3 Broccoli 0-QUAD 3 Horseradish C)07120/05 07120105 MEAN 07/20105 07120105 MEAN 07120105 07/20/05 MEAN 07/20105 07/20/05 MEAN 07/20105 07/20105< 20< 14 17 +/- 9< 18< 21 20 +/- 4< 26< 15 20 +/- 15< 20< 5 12 +/- 20< 25< 12< 15< 13 14 +/- 4< 19< 23 21 +/- 6< 21< 15 18 +/- 7< 16< 5 11 +/- 16< 25< 16< 24< 31 27 +/- 11< 35< 41 38 +/- 8< 49< 31 40 +/- 25< 40< 12 26 +/- 39< 40< 29 CO-60<18<17 17 +/- 2< 18< 35 27 +/- 24< 35< 16 25 +/- 27< 18< 6 12 +/- 18< 21< 9 ZN-65< 26< 33 30 +/- 10< 44< 52 48 i 12< 68< 32 50 +/- 51< 41< 12 27 i 40< 54< 23 ZRNB-95< 17< 17 17 +/- 1< 20< 24 22 +/- 6< 24< 16 20 +/- 12< 21< 6 13 +/- 22< 21< 13 1-131< 36< 34 35 +/- 2< 34< 43 38 +/- 12< 39< 32 35 +/- 9<36< 9 22 +/- 38< 40<24 CS-1 34 CS-137 BALA140< 19< 15 17 +/- 5< 17< 19 18 +/- 3< 17<15 16 +/- 3<17< 5 11 +/- 17< 24< 11< 20< 21 21 +/-I1< 20< 28 24 +/- 10< 22< 19 21 +/- 5< 18< 6 12 +/- 18< 23< 11<32< 24 28 +/- 12< 29< 31 30 +/- 4< 26< 21 23

  • 7< 33< 6 20 +/- 37<36<15 0-QUAD 4 Cabbage 0-QUAD 4 Potatoes 0-QUAD 1 -CONTROL Rhubarb Leaves 0-QUAD 1 -CONTROL Potatoes 00 Lh 0 t-h MEAN 19+/-i18 20 +/-13 35+/- 15 15 +/-16 38+/-i44 17 +/-12 32 +/-24 17+/-i18 17 +/-17 25+/-t29 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 CODE 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-07-1 Q-07-2 Q-13-1 Q-13-2 Q-16-1 0-16-2 Q-37-1 Q-37-2 Q-38-1 Q-38-2 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 Q-106-2 Q-106-3 Q-107-2 Q-107-3 Q-108-1 0-108-2 Q-109-1 Q-109-2 Q-111-1 Q-111-2 Q-112-1 Q-112-2 0-113-1 Q-113-2 0-114-1 Q-114-2 Q-115-1 Q-115-2 Q-116-1 Q-116-3 MEAN i2 S.D.21.3 8.7 20.8 7.7 22.3 8.2 20.5 6.0 20.8 8.1 20.0 8.2 21.8 7.5 21.5 7.4 19.7 7.6 20.0 8.7 21.3 7.5 21.0 8.2 20.0 8.5 20.3 7.0 21.3 10 19.5 +/- 5.8 21.8 +/- 11 20.5 +/- 5.3 20.5 +/- 7.0 21.5 +/- 8.4 22.5 +/- 9.5 21.0 +/- 9.1 20.3 +/- 7.7 20.5 +/- 8.4 20.0 +/- 8.5 20.8 +/- 7.2 21.3 +/- 8.7 20.8 +/- 8.9 20.3 +/- 5.5 19.8 +/- 6.4 21.0 +/- 10 21.0 +/- 8.2 21.3 +/- 10 21.5 +/- 9.9 21.8 +/- 8.2 21.3 +/- 5.3 22.8 +/- 6.6 21.8 +/- 9.1 22.0 +/- 7.3 20.5 +/- 7.0 20.8 +/- 6.6 21.3 +/- 6.8 20.0 +/- 6.3 21.8 +/- 6.0 20.5 +/- 6.8 21.3 +/- 5.3 22.0 +/- 8.5 21.8 +/- 10 JAN-MAR APR-JUN JUL-SEP OCT-DEC 25 25 26 23 23 23 23 24 (1)(1)24 24 22 22 24 22 27 23 23 26 29 27 23 23 22 23 25 25 22 23 26 25 28 27 27 24 26 24 24 23 24 24 22 25 25 25 27 27 17 17 17 17 16 17 17 17 17 17 18 17 16 16 17 17 17 17 17 17 19 17 16 16 16 16 18 16 17 17 16 17 16 16 17 19 19 17 18 17 17 17 16 18 17 20 18 17 18 18 21 19 19 16 21 20 18 18 18 18 17 19 17 17 17 20 18 19 19 18 18 18 17 20 17 18 19 17 17 18 19 19 21 19 21 19 20 18 19 20 19 21 19 19 19 18 25 23 25 23 25 24 26 25 24 25 25 25 25 24 27 22 26 22 24 24 23 22 24 25 25 24 25 24 23 22 25 24 22 24 22 23 25 27 26 24 23 24 23 23 21 21 24 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 CODE MEAN+/- 2 S. D.JAN -MAR APR-JUN JUL-SEP OCT-DEC Q-201-1 Q-201-2 Q-202-1 Q-202-2 0-203-1 Q-203-2 Q-204-1 Q-204-2 Q-205-1 Q-205-4 Q-206-1 Q-206-2 Q-207-1 0-207-4 Q-208-1 Q-208-2 Q-209-1 Q-209-4 Q-210-1 Q-210-4 Q-211-1 Q-211-2 0-212-1 Q-212-2 Q-213-1 Q-213-2 0-214-1 0-214-2 Q-215-1 0-215-2 0-216-1 Q-216-2 22.8 +/- 6.6 22.8 +/- 9.7 20.8 +/- 8.2 19.5 +/- 7.0 21.3 +/- 7.2 25.8 +/- 8.5 22.3 +/- 6.2 24.3 +/- 7.0 23.5 +/- 7.7 24.3 +/- 6.6 22.3 +/- 4.4 22.0 +/- 8.5 23.0 +/- 5.2 22.5 +/- 8.7 22.3 +/- 9.1 23.0 +/- 5.7 22.3 +/- 10.1 22.3 +/- 6.2 21.8 +/- 7.5 23.0 +/- 7.3 26.0 +/- 9.9 25.8 +/- 8.4 23.0 +/- 9.2 20.3 +/- 7.7 21.8 +/- 7.2 21.3 +/- 7.7 22.5 +/- 8.2 24.5 +/- 5.3 21.5 +/- 5.8 25.3 i 7.5 22.0 +/- 7.3 23.8 +/- 8.5 26 29 26 23 26 31 25 26 28 28 25 25 24 26 27 25 28 24 25 27 31 30 27 23 24 25 25 25 24 29 24 27 19 18 16 16 19 21 18 20 19 21 20 17 20 17 17 19 18 18 19 19 20 20 19 16 17 17 19 22 19 22 18 18 21 20 20 17 18 24 22 23 22 22 21 20 22 21 20 23 (2)22 18 21 24 26 19 18 21 19 19 23 19 22 20 23 25 24 21 22 22 27 24 28 25 26 23 26 26 26 25 25 43 25 25 25 29 27 27 24 25 24 27 28 24 28 26 27 (3)(2) TLD NOT CHANGED (3) TLD WAS IN SERVICE 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 CODE INNER RING OUTER RING OTHER CONTROL JAN-MAR APR-JUN JUL-SEP OCT-DEC 24.8 +/- 3.8 17.1 +/-2.1 18.8 +/- 2.3 23.7 +/- 2.8 26.2 i 4.4 18.7 +/- 3.3 20.4 i 7.1 25.3 i 3.9 23.8 +/- 2.9 16.9 +/- 1.0 18.4 +/- 3.0 24.5 +/- 2.8 (1)17.0 +/- 0.0 18.0 +/- 0.0 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 INNER RING OUTER RING OTHER CONTROL SAMPLES ANALYZED 120 126 64 6 PERIOD MINIMUM 16 16 16 17-PERIOD MAXIMUM 29 31 27 25 PERIOD MEAN 21.1 +/- 7.1 22.8 +/- 7.3 20.9 +/- 7.1 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 JUL-SEP OCT-DEC 04/15/05 07/15/05 10/06/05 04/15/05 07/15/05 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 PERIOD Q-01 Q-02 Q-03 Q-04 0-07 1 12131/04 -01/07/05

--12/31/04 -01/07/05 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 3 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 5 01/28/05 -02104/05 01/28/05 -02104/05 01/28/05 -02104/05 6
  • 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 8
  • 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 10
  • 03/04/05 -03/11/05 03/04/05 -03/11/05 03/04/05 -03/11/05 11 03/11/05 -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 13 03/25/05 -04/02/05 03/25/05 -04/02/05 03/25/05 -04/02/05 14
  • 04/02/05 -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 16
  • 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 18
  • 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 20
  • 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 22
  • 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 24
  • 06/11/05 -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 26
  • 06/24/05 -07/02/05 06/24/05 -07/02/05 06/24/05 -07/02/05 27 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 29 07115/05 -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 31 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 33 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 35 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 37 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 39 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 41 (1) 10/07/05 -10/14/05 10/07/05 -10/14/05 42 (1) 10/14/05 -10/21/05 10/14/05 -10/21/05 43 10/21105 -10/28/05 10/21/05 -10/28/05 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 45 11/04/05 -11/11/05 11/04/05 -11/11/05 10/28/05 -11/04/05 46
  • 11/11/05 -11/18/05 11/11/05 -11/18/05 11/04/05 -11/11/05 47 11/18/05 -11/25/05 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 49 12/02/05 -12/09/05 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 51 12/16/05 -12/23/05 12/16/05 -12/23/05 12116/05 -12/23/05 52
  • 12/23/05 -12/30/05 12/23/05 -12/30/05 12/23/05 -12/30/05 12/31/04 -01107/05 01/07/05 -01/14/05 01/14/05 -01/21/05 01/21/05 -01/28/05 01/28/05 -02/04/05 02/04/05 -02/11/05 02/11/05 -02/18/05 02/18/05 -02/26/05 02/26/05 -03/04/05 03/04/05 -03/11/05 03/11/05 -03/18/05 03/18/05 -03/25/05 03/25105 -04/02/05 04/02/05 -04/08/05 04/08/05 -04/15/05 04/15/05 -04/22/05 04/22/05 -04/29/05 04/29/05 -05/06/05 05/06/05 -05/13/05 05/13/05 -05/20/05 05/20/05 -05/27/05 05/27/05 -06/03/05 06/03/05 -06/11/05 06/11/05 -06/17/05 06/17/05 -06/24/05 06/24/05 -07/02/05 07/02/05 -07/08/05 07/08/05 -07/15/05 07/15/05 -07/22/05 07/22/05 -07/29/05 07/29/05 -08/05/05 08/05/05 -08/1205 08/12/05 -08/19/05 08/19/05 -08/26/05 08/26/05 -09/02/05 09/02/05 -09/09/05 09/09/05 -09/16/05 09/16/05 -09/23/05 09/23/05 -09/30/05 09/30/05 -10/07/05 09/30/05 -10/07/05 10/07/05 -10/14/05 10/14/05 -10/21/05 10/21/05 -10/28/05 10/28/05 -11/04/05 11/04/05 -11/11/05 11/11/05 -11/18/05 11/18/05 -11/25/05 11/25/05 -12/02/05 12/02/05 -12/09/05 12/16/05 -12/23/05 12/23/05 -12/30/05 12/31/04 -01/07/05 01/07/05 -01/14/05 01/14/05 -01/21/05 01/21/05 -01/28/05 01/28/05 -02/04/05 02/04/05 -02/11/05 02/11/05 -02/18/05 02/18/05 -02/26/05 02/26/05 -03/04/05 03/04/05 -03/10/05 03/10/05 -03/18/05 03/18/05 -03/25/05 03/25/05 -04/01/05 04/01/05 -04/08/05 04/08/05 -04/15/05 04/15/05 -04/22/05 04/22/05 -04/29/05 04/29/05 -05/06/05 05/06/05 -05/13/05 05/13/05 -05/20/05 05/20/05 -05/27/05 05/27/05 -06/03/05 06/03/05 -06/09/05 06/09/05 -06/17/05 06/17/05 -06/24/05 06/24/05 -07/01/05 07/02/05 -07/08/05 07/08/05 -07/15/05 07/15/05 -07/22/05 07/22/05 -07/29/05 07/29/05 -08/05/05 08/05/05 -08/12/05 08/12/05 -08/19/05 08/19/05 -08/26/05 08/26/05 -09/02/05 09/02/05 -09/09/05 09/09/05 -09/16/05 09/16/05 -09/23/05 09/16/05 -09/23/05 09/23/05 -09/30/05 09/30/05 -10/07/05 10/07/05 -10/14/05 10/14/05 -10/21/05 10/21/05 -10/28/05 10/28/05 -11/03/05 11/03/05 -11/11/05 11/11/05 -11/18/05 11/18/05 -11/25/05 11/25/05 -12/02/05 12/02/05 -12/09/05 12/16/05 -12/23/05 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 CODE Q-01 -1 Q-01-2 Q-02-1 Q-02-2 Q-03-1 Q-03-2 Q-04-1 Q-04-2 0-13-1 Q-13-2 Q-16-1 Q-16-2 Q-37-1 Q-37-2 0-38-1 Q-38-2 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 Q-106-2 Q-106-3 Q-107-2 Q-107-3 Q-108-1 0-108-2 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-116-3 JAN -MAR APR -JUN JUL -SEP OCT -DEC 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01105 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01106 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 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 CODE Q-201 -1 Q-201-2 Q-202-1 Q-202-2 Q-203-1 Q-203-2 0-204-1 Q-204-2 Q-205-1 Q-205-4 Q-206-1 Q-206-2 Q-207-1 Q-207-4 Q-208-1 0-208-2 0-209-1 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 Q-214-1 0-214-2 Q-215-1 Q-215-2 0-216-1 Q-216-2 JAN -MAR APR -JUN JUL -SEP OCT -DEC 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 01/01/05 -04/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 04/01/05 -07/01/05 07/01/05 -10/01/05 07/01/05 -10/01/05 07/01/05-10/01/05 07/01/05-10/01/05 07/01/05 -10/01/05 07/01/05 -10/01/05 07/01/05 -10/01/05 07/01/05 -10/01/05 07/01/05 -10/01/05 07/01/05 -10/01/05 07/01/05 -10/01/05 07/01/05 -10/01/05 07/01/05 -10/01/05 07/01/05 -10/01/05 07/01/05-10/01/05 07/01/05-10/01/05 07/01/05 -10/01/05 07/01/05-10/01/05 07/01/05 -10/01/05 07/01/05-10/01/05 07/01/05 -10/01/05 07/01/05 -10/01/05 07/01/05 -10/01/05 07/01/05 -10/01/05 07/01/05 -10/01/05 07/01/05 -10/01/05 07/01/05 -10/01/05 07/01/05 -10/01/05 07/01/05 -10/01/05 07/01/05 -10/01/05 07/01/05 -10/01/05 07/01/05 -10/01/05 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 10/01/05 -01/01/06 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 01-00 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 +U c.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 0.200 100-100 ~-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 0.200 +100 +0+-100]--01-01-00 I I 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 400-300-200-C)C.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 0~la 500 400 300 200 100 \ / /-100-200 I I i .I , 01-01-00 12:31-00 12-31-0-1 12-31-02 12-31403 12-30 0-04 Q-36 Cordova Well 4.500 400 300 200 100-100-200 i I 01-01-00 12-31-00 12-31-01 l I I l 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 12-31 -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 CL 119 us v-40.0 4 30.0 4 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'Station 0-01 lost power 10-07-05 21-05.1-05 Q-02 Onsite No. 2 60.0 -r 50.0.a.9 III CD 40.0*30.0 -1.20.0 +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 08-19-05 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 I4 6.0 4.0 IVQ5 I 2.0 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 -I v.6.0-4.0-,!I -, 2.01 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 +U a.C?cI of 40.0 *4.30.0 +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 IN JULY 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 CL rb 9o 50.0 40.0 30.0 +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 9 Uj!9 40.0 +30.0 +20.0 +10.0 +0.0 I-12-31-04 0 0 0 .1 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 IN JULY 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 E4523-396 Milk E4525-396 AP Sr-89 Sr-90 1-131 Ce-141 Cr-51 Cs-134 Cs-1 37 Co-58 Mn-54 Fe-59 Zn-65 Co-60 Ce-141 Cr-51 Cs-134 Cs-1 37 Co-58 Mn-54 Fe-59 Zn-65 Co-60 pCi/L 96.9 107 pCi/L 16.9 17.9 pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi pCi pCi pCi pCi pCi pCi pC!pCi 82.7 217 314 123 125 110 158 118 191 140 150 278 105 95.6 84.4 112 92.8 162 102 92.3 229 334 139 130 115 160 111 198 144 172 250 104 97.1 86.3 120 83.2 148 108 0.91 0.94 0.90 0.95 0.94 0.89 0.96 0.96 0.99 1.06 0.96 0.97 0.87 1.11 1.01 0.98 0.98 0.93 1.12 1.09 0.94 1.11 E4524-396 Charcoal 1-131 pCi 67.4 60.7 June 2005 E4630-396 Milk Sr-89 Sr-90 pCi/L 89.4 88.1 pCi/L 11.6 11.4 1.01 1.02 A A E4631-396 Milk E4633-396 AP 1-131 Ce-1 41 Cr-51 Cs-134 Cs-137 Mn-54 Fe-59 Zn-65 Co-60 Ce-141 Cr-51 Cs-134 Cs-137 Mn-54 Fe-59 Zn-65 Co-60 pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi pCi pC!pCi pCi pCi pCi pCi 82.3 91.6 278 81.1 180 124 61.1 156 136 79.2 263 69.7 135 94.9 48 120 104 86.9 92.4 303 95.0 189 125 63.9 155 145 64.2 210 66.1 131 87.0 44.4 108 101 0.95 0.99 0.92 0.85 0.95 0.99 0.96 1.01 0.94 1.23 1.25 1.05 1.03 1.09 1.09 1.11 1.03 A A A A A A A A A w W A A A A A 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 Month/Year Number Matrix Nuclide Reported Known -Ratio (c)Units Value (a) Value (b) TBE/Analytics Evaluation (d)September 2005 E4766-396 Milk E4767-396 Milk E4769-396 AP Sr-89 Sr-90 1-131 Ce-141 Cr-51 Cs-134 Cs-1 37 Co-58 Mn-54 Fe-59 Zn-65 Co-60 Ce-141 Cr-51 Cs-134 Cs-137 Co-58 Mn-54 Fe-59 Zn-65 Co-60 pCi/L 135.0 146.0 pCi/L 9.7 11.5 pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pci pci pci pci pC pC pC pci pci 87.5 203 279 102 178 55.3 81.8 59.9 120 146 193 267 78.4 166 53.7 81.6 59.6 107 133 94.3 233 338 122.0 195 63.4 92.0 61.0 123 167 169 246 88.8 142 46.0 66.8 44.3 89.6 122 0.92 0.84 0.93 0.87 0.83 0.84 0.91 0.87 0.89 0.98 0.98 0.87 1.14 1.09 0.88 1.17 1.17 1.22 1.35 1.19 1.09 1.00 A A A A A A A A A A A A A A A A A W N (1)A A A E4768-396 Charcoal 1-131 pCi 63.9 64.2 December 2005 E4766-396 Milk E4767-396 Milk E4633-396 AP Sr-89 Sr-90 1-131 Ce-141 Cr-51 Cs-134 Cs-137 Co-58 Mn-54 Fe-59 Zn-65 Co-60 Ce-141 Cr-51 Cs-134*Cs-137 Co-58 Mn-54 Fe-59 Zn-65 Co-60 pCi/L 114 128 pCi/L 11.6 10.3 pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L 79.6 202 185 74.9 177 73.9 152 97.5 161 102 74.6 224 193 87.3 189 77.5 152 82.4 154 ill 201 173 78.3 170 69.4 137 73.9 138 99.1 0.89 1.13 1.07 0.90 0.96 0.86 0.94 0.95 1.00 1.18 1.05 0.92 1.10 1.13 0.87 1.14 1.12 1.25 1.27 1.25 1.10 A A A A A A A A A A A A A A A A A W W W A pCi 221 pCi 195 pCi 68.4 pCi 194 pCi 77.4 pCi 171 pCi 94.2 pCi 173 pCi 109 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 Sr-90 Ba-1 33 Cs-134 Cs-137 Co-60 Zn-65 Gr-A Gr-B H-3 pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L 37.5 5.37 88.6 70.5 201 37.5 122 35.5 35.6 24600 41.3 5.92 88.4 78.6 201 37.0 118 37.0 34.2 24400 32.6 -50.0 0.00 -14.6 73.1 -104 69.9 -87.3 184 -218 28.3 -45.7 97.6- 138 21.0 -53.0 25.5 -42.9 20200 -28600 A A A A A A A A A A Rad 61 Water 1-131 pCi/L 13.6 15.5 10.3 -20.7 A November 2005 Rad 63 Water Sr-89 Sr-90 Ba-133 Cs-134 Cs-1 37 Co-60 Zn-65 Gr-A Gr-B H-3 pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L 18.0 16.6 31.7 30.8 26.8 83.9 109 19.5 34.0 12400 19.0 16.0 31.2 33.9 28.3 84.1 105 23.3 39.1 12200 10.3 -27.7 7.37 -24.7 22.5 -39.9 25.2 -42.6 19.6 -37.0 75.4 -92.8 86.8 -123 13.2 -33.4 30.4 -47.8 10100 -14300 A A A A A A A A A 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 Cs-137 Co-57 Co-60 H-3 Mn-54 Sr-90 Zn-65 Bq/L Bq/L Bq/L Bq/L Bq/L Bq/L Bq/L Bq/L Bq/L Bq/L Bq/L Bq/L Bq/L Bq/L Bq/L 108 305 215 241 283 314 0.093 509 655 310 234 219 512 642 890 127 88.90 -165.10 332 232.40 -461.60 227 158.90 -295.10 251 175.70 -326.30 280 196.00 -364.00 331 231.70 -430.30 no range given (1)496 347.20 -644.80 MaS13 Soil Cs-1 34 Cs-137 Co-57 Co-60 Mn-54 K-40 Zn-65 759 315 242 212 485 604 810 531.30 -986.70 220.50 -409.50 169.40- 314.60 148.40 -275.60 339.50 -630.50 422.80 -785.20 567.00 -1053 GrW13 Water Gr-A Gr-B Bq/L 0.601 0.525 >0.0 -1.05 Bq/L 1.54 1.67 0.84 -2.51 RdF13 GrF13 AP Cs-1 34 Cs-1 37 Co-57 Co-60 Mn-54 Sr-90 Zn-65 AP Gr-A Gr-B Bq/sample Bq/sample Bq/sample Bq/sample Bq/sample Bq/sample Bq/sample 3.26 2.05 4.78 3.02 3.31 1.15 3.14 3.51 2.26 4.92 3.03 3.33 1.35 3.14 2.46 -4.56 1.58 -2.94 3.44 -6.40 2.12-3.94 2.33 -4.33 0.95- 1.76 2.20 -4.08 Bq/sample 0.0764 0.232 >0.0 -0.46 Bq/sample 0.305 0.297 0.15 -0.45 April 2005 RdV1 3 Vegetation Cs-134 Cs-1 37 Co-57 Co-60 Mn-54 Sr-90 Zn-65 Bq/kg Bq/kg Bq/kg Bq/kg Bq/kg Bq/kg Bq/kg 5.45 4.80 13.4 3.67 6.45 1.49 7.71 5 4.1 9.88 3.15 5.18 1.65 6.29 3.50 -6.50 2.88 -5.34 6.92 -12.84 2.21 -4.10 3.63 -6.73 1.16 -2.15 4.40 -8.18 A A A*A A A A October 2005 05-MaW14 Water Cs-134 Cs-1 37 Co-57 Co-60 H-3 Mn-54 Sr-90 Zn-65 Bq/L Bq/L Bq/L Bq/L Bq/L Bq/L Bq/L Bq/L 142 302 251 243 547 383 8.75 324 167 333 272 261 527 418 8.98 330 116.90 -217.10 233.10 -432.90 190.40 -353.60 182.70 -339.30 368.90 -685.10 292.60 -543.40 6.29 -11.67 231.00 -429.00 A A A A A A A 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 Cs-1 37 Co-57 Co-60 Mn-54 K-40 Zn-65 Bq/L Bq/L Bq/L Bq/L Bq/L Bq/L Bq/L 494 446 506 289 460 626 889 568 439 524 287 439 604 823 397.60 -738.40 307.30 -570.70 366.80 -681.20 200.90 -373.10 307.30 -570.70 422.80 -785.20 576.10- 1070 A A A A A A A GrW14 Water Gr-A Gr-B Bq/L 0.858 0.79 Bq/L 1.22 1.35 0.21 -1.38 0.85 -1.92 A A October 2005 RdF14 AP Cs-1 34 Cs-137 Co-57 Co-60 Mn-54 Sr-90 Zn-65 Bq/sample Bq/sample Bq/sample Bq/sample Bq/sample Bq/sample Bq/sample 4.11 3.16 6.14 2.86 4.54 2.12 4.28 3.85 3.23 6.2 2.85 4.37 2.25 4.33 2.70 -5.01 2.26 -4.20 4.34 -8.06 2.00 -3.71 3.06 -5.68 1.58 -2.93 3.03 -5.63 A A A A A A A GrF14 AP Gr-A Gr-B Bq/sample 0.304 0.482 >0.0 -0.80 Bq/sample 0.858 0.827 0.55 -1.22 RdV1 3 Vegetation Cs-134 Cs-1 37 Co-57 Co-60 Mn-54 Sr-90 Zn-65 Bq/kg Bq/kg Bq/kg Bq/kg Bq/kg Bq/kg Bq/kg 4.35 5.99 17.0 4.87 7.40 2.03 11.8 4.09 5.4 13.30 4.43 6.57 2.42 10.2 2.86 -5.32 3.80 -7.06 9.31 -17.29 3.10-5.76 4.60 -8.54 1.69 -3.15 7.14 -13.26 A A A A W A A A 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 STW-1051 STW-1052 STW-1052 STW-1052 STW-1052 STW-1052 STW-1053 STW-1053 STW-1054 STW-1054 STW-1054 STW-1055 STW-1055 STW-1056 STW-1056 STW-1056 STW-1056 STW-1056 STW-1057 STW-1057 STW-1058 STW-1059 STW-1059 STW-1059 STW-1060 STW-1067 STW-1067 STW-1068 STW-1068 STW-1068 STW-1068 STW-1068 STW-1069 STW-1069 STW-1070 STW-1070 STW-1070 02/15/05 02/15/05 02/15/05 02/15/05 02/15/05 02/15/05 02/15/05 02/15/05 02/15/05 02/15/05 02/15/05 02/15/05 05/17/05 05/17/05 05/17/05 05/17/05 05/17/05 05/17/05 05/17/05 05/17/05 05/17/05 05/17/05 05/17/05 05/17/05 05/17/05 05/17/05 08/16/05 08/16/05 08/16/05 08/16/05 08/16/05 08/16/05 08/16/05 08/16/05 08/16/05 08/16/05 08/16/05 08/16/05 Sr-89 Sr-90 Ba-133 Co-60 Cs-134 Cs-137 Zn-65 Gr. Alpha Gr. Beta Ra-226 Ra-228 Uranium Sr-89 Sr-90 Ba-133 Co-60 Cs-134 Cs-137 Zn-65 Gr. Alpha Gr. Beta 1-131 Ra-226 Ra-228 Uranium H-3 Sr-89 Sr-90 Ba-133 Co-60 Cs-134 Cs-137 Zn-65 Gr. Alpha Gr. Beta Ra-226 Ra-228 Uranium 28.0 +/- 1.2 25.1 +/-0.7 52.9 +/- 2.8 54.4 +/- 0.4 67.7 +/- 1.8 39.6 +/- 1.8 159.7 +/- 3.0 55.1 +/- 1.8 46.8 +/- 1.3 13.7 +/- 1.5 13.3 +/- 0.6 5.1 +/-0.2 45.1 +/-4.1 7.5 +/- 0.9 87.1 +/-2.0 38.4 +/- 0.8 75.3 +/- 0.7 201.0 +/- 8.4 130.0 +/- 6.7 42.7 +/- 2.9 34.0 +/- 0.4 14.7 +/- 0.5 6.6 +/- 0.1 19.3 +/- 0.7 9.6 +/-0.1 24100.0 +/- 109.0 29.1 +/-3.0 36.0 +/- 0.6 107.0 +/- 1.7 15.2 +/- 0.2 89.1 +/-0.3 72.1 +/- 1.0 67.4 +/- 1.4 44.3 +/- 1.5 58.4 +/- 2.1 16.6 +/- 1.5 6.2 +/- 0.3 4.5 +/- 0.1 29.4 24.4 53.4 56.6 64.9 40.2 161.0 67.9 51.1 14.1 13.7 5.0 41.3 5.9 88.4 37.0 78.6 194.0 118.0 37.0 34.2 15.5 7.6 18.9 10.1 24400.0 28.0 33.8 106.0 13.5 92.1 72.7 65.7 55.7 61.3 16.6 6.2 4.5 20.7 -38.1 15.7 -33.1 44.2 -62.6 47.9 -65.3 56.2 -73.6 31.5 -48.9 133.0 -189.0 38.5 -97.3 38.5 -97.3 10.4 -17.8 7.8 -19.6 0.0 -10.2 32.6 -50.0 0.0 -14.6 73.1 -104.0 28.3 -45.7 69.9 -87.3 184.0 -218.0 97.6 -138.0 21.0 -53.0 25.5 -42.9 10.3 -20.7 5.6 -.9.5 10.7 -27.1 4.9 -15.3 20200.0 -28600.0 19.3 -36.7 25.1 -42.5 87.7 -124.0 4.8 -22.2 83.4 -101.0 64.0 -81.4 54.3 -77.1 31.6 -79.8 44.0 -78.6 12.3 -20.9 3.5 -8.9 0.0 -9.7 Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass 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 STW-1045 01/01/05 Gr. Beta 0.45 +/- 0.10 1.90 +/- 0.10 0.53 1.67 0.00 -1.05 0.84 -2.51 Pass Pass STW-1046 STW-1046 STW-1046 STW-1046 STW-1046 STW-1046 STW-1046 STW-1046 STW-1046 STW-1046 STW-1046 STW-1046 STW-1046 STW-1046 STW-1046 STW-1046 STVE-1047 STVE-1047 STVE-1047 STVE-1047 STVE-1047 STVE-1047 STSO-1048 STSO-1048 STSO-1048 STSO-1048 STSO-1048 STSO-1048 STSO-1048 STSO-1048 STSO-1048 STSO-1048 STSO-1048 STSO-1048 STSO-1048 STSO-1048 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 Am-241 Co-57 Co-60 Cs-1 34 Cs-1 37 Fe-55 H-3 Mn-54 Ni-63 Pu-238 Pu-239/40 Sr-90 Tc-99 U-233/4 U-238 Zn-65 Co-57 Co-60 Cs-134 Cs-137 Mn-54 Zn-65 Am-241 Co-57 Co-60 Cs-1 34 Cs-137 K-40 Mn-54 Ni-63 Pu-238 Pu-239/40 Sr-90 U-233/4 U-238 Zn-65 1.62 +/- 0.12 239.40 +/- 1.20 248.70 +/- 1.00 115.50 +/- 1.80 328.50 +/- 1.70 64.90 +/- 7.00 304.00 +/- 9.70 334.80 +/- 1.90 7.10 +/- 1.60 0.01 +/- 0.02 2.50 +/- 0.14 0.70 +/- 0.80 43.20 +/- 1.40 3.31 +/- 0.20 3.38 +/- 0.20 538.40 +/- 3.80 10.60 +/- 0.20 3.00 +/- 0.20 4.80 +/- 0.40 4.10 +/- 0.30 5.10 +/- 0.30 6.20 +/- 0.50 96.60 +/- 10.00 264.00 +/- 2.00 226.50 +/- 2.20 760.60 +/- 3.70 336.20 +/- 3.60 663.70 +/- 18.00 541.30 +/- 3.90 924.30 +/- 17.20 0.60 +/- 0.80 78.00 +/- 4.80 514.60 +/- 18.70 47.90 +/- 4.00 226.30 +/- 8.60 851.30 +/- 7.30 1.72 227.00 251.00 127.00 332.00 75.90 280.00 331.00 9.00 0.02 2.40 0.00 42.90 3.24 3.33 496.00 9.88 3.15 5.00 4.11 5.18 6.29 109.00 242.00 212.00 759.00 315.00 604.00 485.00 1220.00 0.48 89.50 640.00 62.50 249.00 810.00 1.20 -2.24 158.90 -295.10 175.70 -326.30 88.90 -165.10 232.40 -431.60 53.13 -98.67 196.00 -364.00 231.70 -430.30 0.00 -20.00 0.00 -1.00 1.68 -3.12 0.00 -5.00 30.03 -55.77 2.27 -4.21 2.33 -4.33 347.20 -644.80 6.92 -12.84 2.21 -4.10 3.50 -6.50 2.88 -5.34 3.63 -6.73 4.40 -8.18 76.30 -141.70 169.40 -314.60 148.40 -275.60 531.30 -986.70 220.50 -409.50 422.80 -785.20 339.50 -630.50 854.00 -1586.00 0.00 -1.00 62.65 -116.35 448.00 -832.00 43.75 -81.25 174.30 -323.70 567.00 -1053.00 Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass STAP-1050 01/01/05 Gr. Alpha STAP-1050 01/01/05 Gr. Beta 0.11 +/- 0.03 0.38 +/- 0.05 0.23 0.30 0.00 -0.46 0.15 -0.45 Pass 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 STAP-1049 STAP-1049 STAP-1049 STAP-1049 STAP-1049 STAP-1049 STAP-1049 STAP-1 049 e STAP-1049 STAP-1049 STAP-1049 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 01/01/05 Am-241 Co-57 Co-60 Cs-134 Cs-137 Mn-54 Pu-238 Pu-239/40 Sr-90 U-233/4 U-238 Zn-65 0.10 +/- 0.04 4.76 +/- 0.64 2.84 +/- 0.22 3.54 +/- 0.37 2.20 +/- 0.27 3.15 +/- 0.21 0.16 +/- 0.04 0.17 +/- 0.02 2.24 +/- 0.34 0.34 +/- 0.02 0.35 +/- 0.02 3.12 +/- 0.15 0.10 4.92 3.03 3.51 2.26 3.33 0.20 0.17 1.35 0.34 0.35 3.14 0.07 -0.13 3.44 -6.40 2.12 -3.94 2.46 -4.56 1.58 -2.94 2.33 -4.33 0.14 -0.25 0.14 -0.25 0.95 -1.76 0.24 -0.44 0.25 -0.46 2.20 -4.08 Pass Pass Pass Pass Pass Pass Pass Pass Fail Pass Pass Pass STW-1061 STW-1061 STW-1061 STW-1061 STW-1061 STW-1061 STW-1061 STW-1061 STW-1061 STW-1061 STW-1061 STW-1061 STW-1061 STW-1061 STW-1061 STW-1061 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 Am-241 Co-57 Co-60 Cs-1 34 Cs-137 Fe-55 H-3 Mn-54 Ni-63 Pu-238 Pu-239/40 Sr-90 Tc-99 U-233/4 U-238 Zn-65 STW-1062 07/01/05 Gr. Alpha STW-1062 07/01/05 Gr. Beta 2.21 +/- 0.13 293.20 +/- 7.30 275.70 +/- 1.30 171.80 +/- 4.00 342.10 +/- 2.20 167.80 +/- 9.30 514.20 +/- 12.60 437.00 +/- 2.50 105.10 +/- 3.60 1.64 +/- 0.12 2.32 +/- 0.13 9.20 +/- 1.30 72.30 +/- 2.30 4.11 +/- 0.18 4.14 +/- 0.18 364.60 +/- 4.90 0.57 +/- 0.05 1.36 +/- 0.05 48.40 +/- 3.90 608.30 +/- 2.80 322.70 +/- 2.40 632.10 +/- 5.20 512.40 +/- 4.20 720.50 +/- 19.00 516.80 +/- 5.10 366.50 +/- 13.30 68.80 +/- 15.00 0.00 +/- 0.00 602.90 +/- 17.20 61.50 +/- 1.00 164.50 +/- 16.70 874.70 +/- 8.40 2.23 272.00 261.00 167.00 333.00 196.00 527.00 418.00 100.00 1.91 2.75 8.98 66.50 4.10 4.26 330.00 0.79 1.35 81.10 524.00 287.00 568.00 439.00 604.00 439.00 445.00 60.80 0.00 757.00 52.50 168.00 823.00 1.56 -2.90 190.40 -353.60 182.70 -339.30 116.90 -217.10 233.10 -432.90 137.20 -254.80 368.90 -685.10 292.60 -543.40 70.00 -130.00 1.34 -2.48 1.93 -3.58 6.29 -11.67 46.55 -86.45 2.87 -5.33 2.98 -5.54 231.00 -429.00 0.21 -1.38 0.85 -1.92 56.77 -105.43 366.80 -681.20 200.90 -373.10 397.60 -738.40 307.30 -570.70 422.80 -785.20 307.30 -570.70 311.50 -578.50 42.56 -79.04 0.00 -0.00 529.90 -984.10 36.75 -68.25 117.60 -218.40 576.10 -1070.00 Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Fail Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass STSO-1063 STSO-1063 STSO-1063 STSO-1063 STSO-1063 STSO-1063 STSO-1063 STSO-1063 STSO-1063 STSO-1063 STSO-1063 STSO-1063 STSO-1063 STSO-1063 t 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 Am-241 Co-57 Co-60 Cs-134 Cs-137 K-40 Mn-54 Ni-63 Pu-238 Pu-239/40 Sr-90 U-233/4 U-238 Zn-65 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 STVE-1064 STVE-1 064 STVE-1064 STVE-1 064 STVE-1064 STVE-1064 STVE-1064 STVE-1064 STVE-1064 STVE-1064 STVE-1064 STAP-1065 STAP-1065 STAP-1066 STAP-1066 STAP-1066 STAP-1066 STAP-1066 STAP-1066 STAP-1066 STAP-1066 STAP-1066 STAP-1066 STAP-1066 STAP- 1066 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 Am-241 Co-57 Co-60 Cs-1 34 Cs-1 37 Mn-54 Pu-238 Pu-239/40 Sr-90 U-233/4 U-238 Zn-65 07/01/05 Gr. Alpha 07/01/05 Gr. Beta 0.18 i 0.03 15.90 i 0.20 4.80 i0.10 4.60 i 0.20 5.90 i 0.30 7.20 i 0.20 0.04 i 0.02 0.13 i 0.02 2.80 i 0.30 0.28 +/- 0.03 0.33 +/- 0.04 11.00 +/- 0.50 0.30 i 0.04 0.97 +/- 0.06 0.14 +/- 0.03 5.81 +/- 0.17 2.79 +/- 0.14 3.67 +/- 0.12 2.93 +/- 0.23 4.11 +/- 0.26 0.11 +/-0.02 0.10 +/- 0.01 2.25 i 0.29 0.28 +/- 0.02 0.28 +/- 0.02 4.11 +/-0.26 0.23 13.30 4.43 4.09 5.43 6.57 0.00 0.16 2.42 0.33 0.35 10.20 0.48 0.83 0.16 6.20 2.85 3.85 3.23 4.37 0.10 0.09 2.25 0.27 0.28 4.33 0.16 -0.30 9.31 -17.29 3.10 -5.76 2.86 -5.32 3.80 -7.06 4.60 -8.54 0.00 -1.00 0.11 -0.21 1.69 -3.15 0.23 -0.43 0.24 -0.45 7.14 -13.26 0.00 -0.80 0.55 -1.22 0.11 -0.21 4.34 -8.06 2.00 -3.71 2.70 -5.01 2.26 -4.20 3.06 -5.68 0.07 -0.13 0.06 -0.12 1.58 -2.93 0.19 -0.35 0.20 -0.37 3.06 -5.68 Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 07/01/05 Am-241 Co-57 Co-60 Cs-134 Cs-1 37 Mn-54 Pu-238 Pu-239/40 Sr-90 U-233/4 U-238 Zn-65*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 (1 sigma, 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)(pCilnm 3)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 (pCi/m 3)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/m 3) 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 <L LD 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 (pC i/mn 3) __ _ _ _ _ _ _ _ _ _ __ _ _ _ __ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ __ _ _ _ _ _ _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 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 of Faciliy 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 (pCi/m 3)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 <LL D <LID 0 a Mean and range based on detectable measurements only. Fractions indicated in parentheses.

I-32 129 of 206

-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 (pCi/mn 3) _ _ _ _ _ _ _ _ _ _ __ _ _ _ _ _ _Milk 1-131 4 5.0 1 0.5 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 1OCFR50 Appendix I, 1OCFR20 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 1 OCFR20 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 limitt 1 1  % 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 41.6jl2. 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 WB7TI 4.92E-02 3.72E-02 4.58E-03 5.77E-05l 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 NA t 2)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 1 1.23E+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 (mi 3) 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 30 65 Mode of Transportation Highway Highway Destination Processor Disposal B. Irradiated Fuel Shipments (disposition)

Number of Shipments 2 Mode of Transportation Highway Destination 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 ............

Year ..................
Coefficient Type ......: Receptor ..............
Distance (meters) .....: Compass Point .........: 1 All Gas Releases 2005 Historical 5 Composite Crit. Receptor -IP 0.0 0.0=== MAXIMUM PERIOD DOSE Dose Age Period Group Organ Quarter__

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

=== MAXIMUM PERIOD DOSE Dose Age Period Group Organ Quarter__

1-CHIL --B--D-Quarter 1 CHILD TBODY Quarter 2 CHILD TBODY Quarter 3 CHILD TBODY Quarter 4 CHILD TBODY Annual CHILD TBODY TO LIMIT Dose (mrem)3.48E-0 1. 60E-0 6.90E-0 2.70E-0 2.91E-0 (Tot Body)Limit Period 3 Quarter 3 Quarter 2 Quarter 3 Quarter 23 Quarter)2 Annual==========2========================

Admin Limit 5. ______5.25E+00 5.25E+00 5.25E+00 5.25E+00 1.05E+01 Admin %of Limit 6. 63E-02 3.05E-01 1.31E-01 5. 14E-02 2. 77E-01 T. Spec Limit 7 _ OE+00 7. 50E+00 7. 50E+00 7. 50E+00 7.50E+00 1. 50E+01 T.Spec %of Limit 4. 64E-02 2.14E-01 9.20E-02 3. 60E-02 1. 94E-01 GASEOUS ANNUAL DOSE

SUMMARY

REPORT (Composite Critical Receptor -Limited Analysis)Release ID ............

1 All Gas Releases Year ..................
2005 Coefficient Type ......: Receptor ..............
Distance (meters) .....: Compass Point .........
Historical 4 Composite 0.0 0.0 Crit. Receptor -NG=== MAXIMUM PERIOD NG Dose Period Dose Type Quarter__

1--Gamma-Quarter 1 Gamma Quarter 2 Gamma Quarter 3 Gamma Quarter 4 Gamma Annual Gamma DOSE TO LIMIT Dose (mrad)7.01E-04 8.99E-05 1.44E-04 2.05E-04 1.14E-03 (Gamma)Limit Period Quarter Quarter Quarter Quarter Quarter Annual=================================

Admin Admin %Limit of Limit________ --------3.75E+00 1.87E-02 3.75E+00 2.40E-03 3.75E+00 3.84E-03 3.75E+00 5.47E-03 7.50E+00 1.52E-02 T.Spec Limit 5.OOE+00 5.OOE+00 5. O0E+00 5. OOE+00 1.OOE+01 T.Spec %of Limit 1.40E-02 1.80E-03 2. 88E-03 4.10E-03 1.14E-02=== MAXIMUM PERIOD NG Dose Period Dose Type Quarter__

1--Beta--Quarter 2 Beta Quarter 3 Beta Quarter 4 Beta Annual Beta DOSE 3 TO LIMIT (Beta)=================================

Dose Limit Admin (mrad) Period Limit 4.12E-04 Quarter 7.50E+00 4.74E-05 Quarter 7.50E+00 6.93E-05 Quarter 7.50E+00 1.25E-04 Quarter 7.50E+00 6.54E-04 Annual 1.50E+01 Admin %of Limit 5.49E-03 6.31E-04 9.24E-04 1. 67E-03 4. 36E-03 T.Spec Limit 1.OOE+01 1. OOE+01 1.00E+01 1. OOE+01 2.00E+01 T.Spec %of Limit 4.12E-03 4.74E-04 6.93E-04 1.25E-03 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 Dose Age Period Group Organ Quarter 1-TEE ---I--ER Quarter I TEEN LIVER Quarter 2 TEEN LIVER Quarter 3 TEEN LIVER Quarter 4 ADULT GILLI Annual TEEN LIVER TO LIMIT (Any Organ) =======-Dose Limit Admin (mrem) Period Limit 4.55E-05 Quarter 3.75E+00 7.21E-05 Quarter 3.75E+00 1.93E-05 Quarter 3.75E+00 1.40E-06 Quarter 3.75E+00 1.13E-04 Annual 7.50E+00== == = = -==== == -----------------

=Admin %of Limit 1. 21E-03 1.92E-03 5. 16E-04 3. 73E-05 1.51E-03 T.Spec Limit 5.00Ei-00 5.OOE+00 5.OOE+00 5.00E+00 1.00E+01 T.Spec %of Limit 9. 09E-04 1. 44E-03 3. 87E-04 2. 80E-05 1.13E-03=== MAXIMUM PERIOD DOSE Dose Age Period Group Organ Quarter 1-ADUL T--DDY-Quarter 1 ADULT TBODY Quarter 2 ADULT TBODY Quarter 3 ADULT TBODY Quarter 4 ADULT TBODY Annual ADULT TBODY TO LIMIT Dose (mrem)2.61E-0 4.64E-0 1.26E-0 8.62E-0 7.05E-0 (Tot Body) ========Limit Admin Period Limit 5 Quarter --------5 Quarter 1.13E+00 5 Quarter 1.13E+00 5 Quarter 1.13E+00 57 Quarter 1.13E+00)5 Annual 2.25E+00:===========================

Admin %of Limit 2.32E-03 4.12E-03 1. 12E-03 7.66E-05 3. 13E-03 T. Spec Limit 1 _ E+00 1.50E+00 1.50E+00 1. 50E+00 1.50E+00 3.00OE+00 T.Spec %of Limit 1.74E-03 3.09E-03 8. 41E-04 5.74E-05 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 10CFR20.1301(a)(1)

Limit 01/01/05 THROUGH 12/31/05 100.0 mrem/year Quad Cities Unit 1 iSt 2 In 3 r 4 t 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)BETA AIR (mrad)WHOLE BODY (mrem)SKIN (mrem)ORGAN (mrem)2.752E-03(WNW) 3.885E-04( N )4.322E-04( SE) 7.050E-05(NNE) 1.720E-03(SSE) 1.920E-02(NNE) 2.245E-03(SSE) 2.265E-02(NNE) 3.156E-04(WNW) 8.333E-04(WNW) 6.650E-04( N )1.015E-04(NNE) 8.562E-03(NNE) 1.016E-02(NNE) 5.248E-04(WNW) 7.050E-04( E )1.260E-04( E )2.583E-03(NNE) 3.077E-03(NNE) 1.636E-04(WNW) 3.894E-03(WNW) 5.997E-04( SE)3.186E-02(NNE) 3.776E-02(NNE) 1.837E-03(WNW)

CRITICAL PERSON CRITICAL ORGAN Teenager Lung Teenager Lung Teenager Lung Teenager Lung Teenager Lung COMPLIANCE STATUS 10 CFR 50 APP. I QUARTERLY OBJECTIVE

% OF APP. I 10 CFR 50 APP.I YEARLY OBJECTIVE TYPE OF DOSE% OF APP. I GAMMA AIR (mrad)BETA AIR (mrad)WHOLE BODY (mrem)SKIN (mrem)ORGAN (mrem)5.0 10.0 2.5 7.5 7.5 0.06 0.00 0.77 0.30 0.01 10.0 20.0 5.0 15.0 15.0 0.04 0.00 0.64 0.25 0 .01 CRITICAL PERSON CRITICAL ORGAN Teenager Lung Teenager 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)BETA AIR (mrad)WHOLE BODY (mrem)SKIN (mrem)ORGAN (mrem)2.752E-03(WNW) 4.322E-04( SE)1.720E-03(SSE) 2.245E-03(SSE) 3.156E-04(WNW) 3.885E-04( N )7.050E-05(NNE) 1.920E-02(NNE) 2.265E-02 (NNE)8.333E-04(WNW) 6.650E-04( N )1.015E-04(NNE) 8.562E-03(NNE) 1.016E-02(NNE) 5.248E-04(WNW) 7.050E-04( E )1.260E-04( E )2.583E-03(NNE) 3.077E-03(NNE) 1.636E-04(WNW) 3.894E-03(WNW) 5.997E-04( SE)3.186E-02(NNE) 3.776E-02(NNE) 1.837E-03(WNW)

CRITICAL PERSON CRITICAL ORGAN Teenager Lung Teenager Lung Teenager Lung Teenager Lung Teenager Lung COMPLIANCE STATUS 10 CFR 50 APP. I QUARTERLY OBJECTIVE

% OF APP. I 10 CFR 50 APP.I YEARLY OBJECTIVE

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

Unit 0 -Vent Unit 0 -Chimney Data Recovery (priority parameters) 98.9%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 N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 1-3 4-7 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0_____6 0 0 0 2 0 1 5 0 8 3 1 14 7 1 0 9 0 8-12 13-18 19-24 > 24 Total_ _ _ _ _ -----0-- --0-- -------0 0 0 0 6 5 0 0 0 5 8 2 0 0 10 5 0 0 0 7 8 0 0 0 8 1 0 0 0 2 6 0 0 0 11 5 0 0 0 5 0 0 0 0 8 1 0 0 0 4 3 0 0 0 4 15 2 0 0 31 14 3 0 0 24 13 0 0 0 23 8 0 0 0 17 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 N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 1-3 4-7 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 4 1 0 0 0 1 2 2 1 0 3 3 3 4 4 2 0 8-12 1 0 0 0 3 3 0 1 1 0 0 4 5 4 1 0 0 13-18 19-24 > 24 Total_____0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0_____0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0--------__ _Total 0 30 23 1 0 0 54 Hours of calm in this stability class: Hours of missing wind measurements in this Hours of missing stability measurements in 0 stability class: 0 all stability classes: 0 152 of 206 Quad Cities Nuclear Station Period of Record: January -March 2005 Stability Class -Slightly Unstable Winds Measured at-196Ft-33Ft Delta-T (F)33 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 4 1 3 1 3 4 1 5 2 2 5 6 4 7 14 12 0 1 0 1 1 0 5 1 2 0 0 0 1 3 11 7 1 0 6 1 4 5 5 10 2 7 2 2 5 8 7 19 22 14 0 Total 5 74 34 6 0 0 119 Hours of calm in Hours of missing this stability class: 0 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 Winds Measured at Wind Speed-196Ft-33Ft Delta-T (F)33 Feet (in mph)Wind Direction N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable Total 1-3 4-7 12 5 7 9 7 7 7 7 10 4 2 3 11 6 6 7 0 110_____22 13 50 42 21 41 19 10 9 10 25 28 34 87 83 45 0 539 8-12 13-18 19-24 > 24 9 3 0 0 8 0 0 0 31 2 0 0 18 2 0 0 18 1 0 0 20 5 0 0 11 0 0 0 4 0 0 0 1 0 0 0 6 0 0 0 8 1 0 0 10 4 0 0 23 8 0 0 63 13 0 0 47 1 0 0 15 0 0 0 0 0 0 0 Total 46 26 90 71 47 73 37 21 20 20 36 45 76 169 137 67 0 981 0 292 40 0 Hours of calm in this stability class: Hours of missing wind measurements in this Hours of missing stability measurements in 0 stability class: 0 all stability classes: 0 154 of 206 Quad Cities Nuclear Station Period of Record: January -March 2005'lass -SliqhtlV Stable -196Ft-33Ft Stability C Delta-T (F)Winds Measured at 33 Feet Wind Direction_________N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable Wind Speed (in mph)1-3 4-7 8-12 13-18 19-24 > 24 Total_ _ _- ------------------------------_ _7 8 13 7 15 14 8 3 6 4 6 10 10 9 6 14 0 19 29 28 28 20 29 6 7 8 4 17 27 10 27 23 18 0 3 13 13 4 10 2 5 1 0 7 S 6 1 2 0 0 0 0 0 1 0 2 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 29 0 51 0 56 0 39 0 45 0 45 0 19 0 11 0 14 0 15 0 31 0 43 0 21 0 38 0 29 0 32 0 0 Total 140 300 72 6 0 0 518 Hours of calm in this stability class: Hours of missing wind measurements in this 0 sta.bility class: 0 stability classes: Hours of missing stability measurements in all 0 155 of 206 Quad Cities Nuclear Station Period of Record: January -March 2005 Stability Class -Moderately Stable Winds Measured at-196Ft-33Ft Delta-T (F)33 Feet Wind Speed (in mph)Wind Direction N NNE NE ENE E ESE SE SSE S SSW SW WSW*W WNW NW NNW Variable 1-3 4-7 0 2 2 7 7 16 6 7 5 4 4 3 7 5 3 1 0 2 0 2 0 2 1 3 8 0 0 1 0 0 1 2 0 0 8-12 13-18 19-24 > 24 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Total 2 2 4 7 9 17 9 15 5 4 5 3 7 6 5 1 0 Total 79 22 0 0 0 0 101 Hours of calm in this stability class: 0 Hours of missing Hours of missing wind measurements in this stability class: 0 stability measurements in all stability classes: 0 156 of 206 Quad Cities Nuclear Station Period of Record: January -March 2005 Stability Class -Extremely Stable Winds Measured at Wind Speed-196Ft-33Ft Delta-T (F)33 Feet (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_____0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0o--------__ _0 1 2 3 7 15 5 4 6 6 6 2 1 3 1 0 0 Total 49 13 0 0 0 0 62 0 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 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 Winds Measured at 296 Feet Delta-T (F)Wind Speed (in mph)Wind Direction 1-3 N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable Total Hours of calm in Hours of missing 4-7 8-12 13-18 19-24 > 24 Total 1__ _ _ 0-- --0-- --0-- --0-- -------1 0 0 0 0 1 0 2 1 0 0 3 0 0 0 0 1 1 0 3 1 0 0 4 0 0 1 0 0 1 0 1 1 0 0 2 3 0 0 1 0 4 0 0 0 0 2 2 1 1 0 0 0 2 0 2 0 0 0 2 2 1 1 1 0 5 1 11 4 0 0 16 0 3 2 8 1 14 1 4 2 2 0 9 1 4 0 0 0 5 0 0 0 0 0 0 0 10 32 13 12 4 71 this stability class: 0 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 Winds Measured at 296 Feet Delta-T (F)Wind Speed (in mph)Wind Direction 1-3 4-7 N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2 1 0 0 0 0 0 1 2 0 2 4 4 1 1 5 0 8-12 13-18 19-24 > 24 2 0 0 0 0 0 0 0 1 0 0 0 1 0 1 1 5 0 0 0 4 0 0 0 2 1 0 0 0 2 3 0 1 0 0 1 2 0 0 0 2 0 0 0 1 5 1 0 4 5 0 1 6 2 6 1 7 3 2 0 2 0 0 0 0 0 0 0 Total 4 1 1 3 5 4 3 6 4 2 4 11 14 16 13 7 0 Total 0 23 40 18 13 4 98 Hours of calm in this stability class: Hours of missing wind measurements in this Hours of missing stability measurements in 0 stability class: 1 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 NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable Total 3 19 22 5 2 21 16 4 4 17 33 41 2 8 22 23 5 13 11 19 9 11 17 22 5 9 10 25 3 7 10 5 1 5 4 6 3 5 6 6 0 4 10 8 0 6 11 13 0 2 23 15 0 19 33 33 1 20 61 64 3 17 39 29 0 0 0 0 2 0 13 6 4 10 3 5 2 8 3 7 12 22 37 7 0 14 1 2 53 0 43 0 108 5 66 0 52 5 74 0 52 7 37 3 21 2 30 3 28 3 40 9 61 20 127 3 186 0 95 0 0 62 1073 35 41 183 328 318 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 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 Winds Measured at 296 Feet Delta-T (F)Wind Speed (in mph)Wind Direction N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 1-3 4-7 8-12 13-18 19-24 > 24 Total 2 5 12 4 0 0 23 0 13 21 5 0 0 39 0 7 19 10 0 0 36 1 6 19 15 2 0 43 4 14 15 12 3 0 48 2 7 11 33 2 0 55 0 4 18 10 0 1 33 0 6 6 7 6 5 30 1 3 9 5 2 0 20 0 1 2 5 2 8 18 0 1 6 16 3 4 30 0 3 4 14 5 0 26 0 2 14 6 3 1 26 0 3 14 7 2 0 26 1 3 17 25 3 0 49 0 5 11 15 1 0 32 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 Winds Measured at 296 Feet Delta-T (F)Wind Speed (in mph)Wind Direction N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 1-3 4-7 1 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2 0 2 3 1 4 3 0 0 1 3 3 1 0 4 1 0 8-12 13-18 19-24 > 24 2 1 0 0 3 1 0 0 3 0 0 0 0 1 0 0 1 1 0 0 9 3 0 0 14 2 0 0 4 4 3 0 15 14 2 0 1 8 2 0 4 2 0 0 1 3 0 0 2 0 0 0 2 0 0 0 3 1 0 0 1 1 0 0 0 0 0 0 Total 6 4 6 4 3 16 19 11 31 12 9 7 3 2 8 3 0 Total 2 28 65 42 7 0 144 Hours of calm in this stability class: Hours of missing wind measurements in this Hours of missing stability measurements in 0 stability class: 2 all stability classes: 77 163 of 206 Quad Cities Nuclear Station Period of Record: January -March 2005 Stability Class -Extremely Stable -296Ft-33Ft Winds Measured at 296 Feet Delta-T (F)Wind Speed (in mph)Wind Direction 1-3 4-7 N 0 1 NNE 0 0 NE 0 0 ENE 1 1 E 0 0 ESE 0 1 SE 0 0 SSE 0 1 S 0 0 SSW 2 3 SW 0 1 WSW 2 0 W 0 0 WNW 0 0 NW 0 2 NNW 0 0 Variable 0 0 8-12 13-18 19-24 > 24 0 0 0 0 0 0 0 0 1 0 0 0 1 0 0 0 0 0 0 0 2 1 0 0 3 2 0 0 2 0 0 0 4 8 1 0 5 8 1 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 2 0 0 0 0 0 0 0 0 0 0 Total 1 0 1 3 0 4 5 3 13 19 1 3 0 0 4 0 0 Total 5 10 19 21 2 0 57 Hours of calm in this stability class: Hours of missing wind measurements in this Hours of missing stability measurements in 0 stability class: all stability cl, 0 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_________N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 1-3 4-7 8-12 13-18 19-24 > 24 Total_ _ _- ------------------------------0 0 4 0 11 4 0 2 6 0 3 4 0 5 8 0 2 14 0 8 11 0 29 9 0 13 9 0 26 17 0 28 14 0 4 17 0 9 17 0 11 31 0 5 4 0 7 5 0 0 0 0 5 0 16 0 14 0 7 0 13 0 16 0 19 0 38 0 22 0 43 0 42 0 21 0 29 0 42 0 12 0 20 0 0 Total 0 163 174 22 0 0 359 Hours of calm in this stability class: Hours of missing wind measurements in this Hours of missing stability measurements in 0 stability class: 0 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 N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 1-3 4-7 0 2 0 4 0 1 0 1 0 0 0 2 0 6 0 2 0 6 0 5 0 4 0 0 0 3 0 2 0 3 0 1 0 0._ --_ _ _0 0 0 0 0 0 0 0 0 0 0 0 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0_ _ _ _ _ -----8-12 13-18 19-24 > 24 Total 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

--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 Winds Measured at-196Ft-33Ft Delta-T (F)33 Feet Wind Speed (in mph)Wind Direction 1-3 4-7 N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 1 2 3 6 4 1 5 3 5 5 10 7 4 2 4 0 0 10 7 10 19 10 21 21 18 13 26 34 26 36 22 12 7 0 8-12 13-18 19-24 > 24 5 5 0 0 11 0 0 0 25 0 0 0 31 0 0 0 10 2 0 0 6 5 0 0 5 0 0 0 2 0 0 0 0 0 0 0 2 0 0 0 7 1 0 0 16 1 0 0 23 1 0 0 30 1 0 0 10 0 0 0 9 1 0 0 0 0 0 0 Total 21 20 38 56 26 33 31 23 18 33 52 50 64 55 26 17 0 Total 62 292 192 17 0 0 563 Hours of calm in this stability class: Hours of missing wind measurements in this Hours of missing stability measurements in 0 stability class: 0 all stability classes: 0 168 of 206 Quad Cities Nuclear Station Period of Record: April -June 2005 Stability Class -Slightly Stable Winds Measured at-196Ft-33Ft Delta-T (F)33 Feet Wind Speed (in mph)Wind Direction N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable Total 1-3 4-7 4 5 1 4 2 8 20 8 12 20 11 34 18 34 15 7 10 19 9 17 10 40 16 27 22 28 18 22 13 20 3 11 0 0 0 3 5 0 5 7 4 2 0 0 9 2 1 3 8 2 0 51 0 0 0 0 0 0 0 0 0 0 0 0 3 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9 8 15 28 40 52 57 24 29 26 60 45 51 43 41 16 0 544 8-12 13-18 19-24 > 24 Total 0 184 304 5 0 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 Quad Cities Nuclear Station Period of Record: April -June 2005 Stability Class -Moderately Stable Winds Measured at-196Ft-33Ft Delta-T (F)33 Feet Wind Speed (in mph)Wind Direction_________N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable Total 1-3 4-7 8-12 13-18 19-24 > 24 Total_____7 9 9 10 17 25 18 11 12 14 8 4 9 9 4 0 0 166_____0 5 3 4 3 30 4 6 6 6 2 0 1 0 1 0 0 7 1_____0 0 0 0 1 1 0 1 0 0 0 0 0 0 0 0 0 3_____0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 7 0 14 0 12 0 14 0 21 0 56 0 22 0 18 0 18 0 20 0 10 0 4 0 10 0 9 0 5 0 0 0 0.0 240 Hours of calm in this stability class: Hours of missing wind measurements in this Hours of missing stability measurements in 0 stability class: 0 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 N 4 0 NNE 4 1 NE 3 0 ENE 9 0 E 18 5 ESE 29 16 SE 10 0 SSE 8 1 S 3 0 SSW 8 0 SW 9 0 WSW 1 0 W 5 1 WNW 5 1 NW 2 0 NNW 0 0 Variable 0 0 8-12 13-18 19-24 > 24 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0_ _ _ _ _ _ _ _ _ _ _ _Total 4 5 3 9 23 45 10 9 3 8 9 1 6 6 2 0 0 143 0 Total 118 25 0 0 0 Hours of calm in Hours of missing Hours of missing this stability class: wind measurements in this stability measurements in 0 stability class: 0 all stability classes: 0 171 of 206 Quad Cities Nuclear Station Period of Record: April -June 2005 Stability Class -Extremely Unstable -296Ft-33Ft Winds Measured at 296 Feet Delta-T (F)Wind Speed (in mph)Wind Direction_________N NNE NE ENE E 1-3_____0 0 0*0.4-7 8-12 13-18 19-24 > 24 Total_ _ _ _ _ -------------------------0 0 0 0 0 1 3 0 1 0 1 0 0 5 0 0 0 0 0 0 0 1 4 6 0 2 0 0 0 2 ESE 0 SE SSE 0 0 0 0 0 0 3 9 5 0 0 3 0 ' 9 0 8 4 11 1 19 S 0 0 2 13 SSW SW WSW W WNW 0 0 0 0 0 1 10 17 2 0 0 1 3 2 4 7 5 3 4 8 0 2 0 3 0 19 0 36 0 12 0 0 9 7 4 13 0 21 NW NNW Variable 0 0 0 0 0 0 3 1 0 0 0 0 5 6 0 1 1 0 9 8 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 -Stability Class -Moderately Unstable Winds Measured at 296 June 2005-296Ft-33Ft Delta-T (F)Feet Wind Speed (in mph)Wind Direction_________N NNE NE ENE E ESE SE 1-3_____0 0 0 0 0 0 0 4-7 8-12 13-18 19-24 > 24 Total_ _ _ _ _ -------------------------0 0 1 0 1 0 1 3 7 2 0 7 3 2 0 2 4 0 4 3 3 0 0 2 0 0 0 1 0 0 0 0 3 9 9 0 0 12 0 0 6 7 SSE 0 S 0 SSW SW WSW W 0 0 0 0 6 2 8 2 2 1 6 2 4 4 2 3 4 1 7 5 3 4 1 3 1 1 0 3 0 0 17 8 1 21 1 13 0 7 1 12 WNW NW NNW Variable 0 0 0 0 0 0 1 0 4 4 5 0 6 1 0 0 5 0 3 0 0 15 0 5 1 10 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 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 N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 0 1 1 3 0 0 1 0 2 2 3 1 1 1 0 2 0-____7 2 6 7 8 5 6 6 9 17 9 6 6 3 4 9 0 8-12 13-18 19-24 > 24 3 5 6 0 6 9 4 0 6 19 14 1 8 19 11 1 10 9 11 1 14 10 6 6 13 7 8 1 6 7 4 0 8 18 6 1 12 12 5 0 11 17 2 2 11 9 13 1 6 30 25 4 7 47 13 10 5 7 11 1 2 10 8 0 0 0 0 0 Total_____21 22 47 49 39 41 36 23 44 48 44 41 72 81 28 31 0 Total 18 110 128 235 147 29 667 Hours of calm in this stability class: Hours of missing wind measurements in this Hours of missing stability measurements in 0 stability class: 1 all stability classes: 49 175 of 206 Quad Cities Nuclear Station Period of Record: April -June 2005 Stability Class -Slightly Stable -296Ft-33Ft Winds Measured at 296 Feet Delta-T (F)Wind Speed (in mph)Wind Direction 1-3 4-7 N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 1 0 0 2 1 1 0 0 1 0 0 1 0 0 1 1 0 1 3 1 1 1 2 3 4 2 0 4 3 4 5 5 6 0 8-12 13-18 19-24 > 24 7 4 0 0 2 2 0 0 5 11 4 0 7 1 0 0 14 13 4 0 16 18 5 1 16 35 7 0 15 17 6 0 23 23 7 0 12 37 3 0 7 26 3 0 7 21 4 0 10 21 1 0 9 12 2 1 16 10 6 1 12 15 1 0 0 0 0 0 Total 13 7 21 11 33 43 61 42 56 52 40 36 36 29 39 35 0 Total 9 45 178 266 53 3 554 Hours of calm in this stability class: Hours of missing wind measurements in this Hours of missing stability measurements in 0 stability class: 1 all stability classes: 49 176 of 206 Quad Cities Nuclear Station Period of Record: April -June 2005 Stability Class -Moderately Stable -296Ft-33Ft Winds Measured at 296 Feet Delta-T (F)Wind Speed (in mph)Wind Direction N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 1-3 4-7 1 1 1 1 1 1 0 1 0 0 1 0 0 1 0 1 0 2 0 3 2 4 3 1 1 1 2 3 1 1 1 4 4 0 8-12 13-18 19-24 > 24 1__ _ _ 0-- --0-- --0-- --1 0 0 0 5 8 0 0 6 4 0 0 9 2 0 0 17 23 9 0 12 30 4 0 5 7 4 0 10 22 3 0 8 18 0 0 2 8 0 0 0 2 0 0 2 6 0 0 2 4 0 0 7 0 0 0 3 0 0 0 0 0 0 0 Total 4 1 17 13 16 53 47 18 36 28 14 3 9 8 11 8 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 Class -Extremely Stable -296Ft-33Ft Winds Measured at 296 Feet Stability Delta-T (F)Wind Speed (in mph)Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total------------------__ _N 1 0 2 NNE 0 0 0 NE 0 0 0 ENE 0 2 6 E 0 0 2 ESE 0 0 2 SE 1 1 1 SSE 0 0 6 S 1 0 5 SSW 0 1 6 SW 0 4 3 WSW 6 2 0 W 1 2 0 WNW 0 0 0 NW 1 0 2 NNW 1 3 0 Variable 0 0 0 2 0 0 0 0 2 8 5 15 6 4 0 0 0 0 0 0 0 5 0 0 0 0 0 8 0 2 0 6 0 13 0 11 0 21 0 13 0 11 0 8 0 3 0 0 0 3 0 4 0 0 0 108 Total 12 15 35 42 Hours of calm in Hours of missing this stability class: 0 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 Class -Extremely Unstable -196Ft-33Ft Stability Delta-T (F)Winds Measured at 33 Feet Wind Speed (in mph)Wind Direction_________N NNE 1-3_____0 0 4-7 8-12 13-18 19-24 > 24 Total_ _ _ _ _ -------------------------7 4 8 9 0 0 0 0 0 15 0 13 NE ENE E ESE 0 14 13 0 1 0 4 3 3 2 7 7 0 0 0 0 0 0 0 0 0 27 0 6 0 11 0 10 SE SSE S SSW SW WSW 0 13 0 39 0 15 0 42 0 31 0 10 4 1 3 7 8 5 4 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 17 0 40 0 18 0 49 0 39 0 15 0 10 0 11 W 0 6 WNW 0 10 NW NNW Variable Total 0 21 0 12 6 2 0 87 0 0 0 0 0 0 0 0 0 27 0 14 0 0 0 0 1 234 0 322 Hours of calm in this stability class: Hours of missing wind measurements in this Hours of missing stability measurements in 0 stability class: 0 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 N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 1-3 4-7 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 4 5 2 3 0 3 2 4 5 4 8 2 2 6 8 7 0 8-12 13-18 19-24 > 24 1__ _ _ 0-- --0-- --0-- --1 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 .0 0 0 0 .0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Total 5 6 2 3 0 3 2 4 5 4 8 2 2 6 8 7 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 Stability Wind Directior Period of Record: July -Septembe Class -Slightly Unstable -196 Winds Measured at 33 Feet Wind Speed (in mph)r 2005 Ft-33Ft Delta-T (F)I 1-3 4-7 8-12 13-18 19-24 > 24 Total I N 0 14 1 0 NNE 0 6 0 0 NE 0 12 1 0 ENE 2 11 1 0 E 0 1 2 0 ESE 0 2 0 0 SE 0 9 1 0 SSE 2 5 0 0 S 0 10 0 0 SSW 2 14 3 0 SW 1 16 0 0 WSW 0 10 0 0 W 0 16 2 0 WNW 0 5 0 0 NW 0 14 1 0 NNW 0 10 0 0 Variable 0 0 0 0-------------__ _0 15 0 6 0 13 0 14 0 3 0 2 0 10 0 7 0 10 0 19 0 17 0 10 0 18 0 5 0 15 0 10 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 N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 1-3 4-7 8-12 13-18 19-24 > 24 Total.2 1 4 6 2 4 4 5 7 4 5 8 5 6 6 5 0 33 19 22 25 16 33 13 14 16 20 23 23 14 19 29 24 0 17 3 6 2 1 2 1 0 0 3 5 1 3 2 6 4 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0o 0 52 0 23 0 32 0 33 0 19 0 39 0 18 0 19 0 23 0 27 0 33 0 32 0 22 0 27 0 41 0 33 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 -Stability Class -Slightly Stable Winds Measured at Wind Speed Wind September 2005-196Ft-33Ft Delta-T (F)33 Feet (in mph)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 8 31 17 14 11 19 11 12 13 5 12 23 19 8 16 5 14 31 5 16 7 23 12 18 14 16 16 21 6 27 6 29 0 0 0 39 0 31 0 30 0 23 0 18 0 35 0 27 0 23 0 46 0 22 0 31 0 30 0 30 0 38 0 33 0 36 0 0 0 492/187 298 6 1 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 Stability Wind Direction Period of Record: July -Class -Moderately Stable Winds Measured at Wind Speed September 2005-196Ft-33Ft Delta-T (F)33 Feet (in mph)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 13 14 10 12 16 28 26 35 16 8 3 9 4 14 12 9 0 229 V 3 0 3 1 2 10 0 1 9 8 0 1 2 2 1 1 0 4 4 0 16 0 14 0 13 0 13 0 18 0 38 0 26 0 36 0 25 0 16 0 3 0 10 0 6 0 16 0 13 0 10 0 0 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 Stability Period of Record: July -Class -Extremely Stable Winds Measured at September 2005-196Ft-33Ft 33 Feet Delta-T (F)Wind Speed (in mph)Wind Direction_________N NNE NE ENE E 1-3_____3 5 6 3 28 4-7 8-12 13-18 19-24 > 24 Total_ _ _ _ _ -------------------------0 0 2 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3 5 8 3 0 28 ESE SE SSE S SSW SW WSW W WNW NW NNW Variable Total 73 33 18 10 0 2 0 7 13 3 4 0 208 0 75 0 33 0 18 0 10 0 0 0 0 0 2 0 7 0 13 0 0 0 3 4 0 0 212 Hours of calm in Hours of missing Hours of missing this stability class: wind measurements in this stability measurements in 0 stability class: 0 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 NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 2 3 4 2 1 0 3 17 2 10 7 1 0 0 3 2 0 0 0 9 0 0 2 2 6 4 28.1 2 1 2 4 2 0 2 3 13 2 1 2 5 24 7 41 9 3 1 2 7 4 0 Total 0 5 57 63 1 0 126 Hours of calm in this stability class: 0 Hours of missing Hours of missing wind measurements in this stability class: 0 stability measurements in all stability classes: 32 186 of 206 Quad Cities Nuclear Station Stability Period of Record: July -September 2005 Class -Moderately Unstable -296Ft-33Ft Winds Measured at 296 Feet Delta-T (F)Wind Speed (in mph)Wind Direction_________N NNE NE ENE E ESE 1-3_____0 0 0 0 0 0 4-7 8-12 13-18 19-24 > 24 Total_ _ _ _ _ -------------------------1 2 3 3 2 0 3 5 5 1 4 1 3 1 2 1 1 1 0 0 0 0 0 0 0 0 7 8 0 10 0 0 0 5 7 2 SE SSE S SSW SW WSW W 0 0 0 0 0 0 0 1 0 2 2 2 1 3 6 6 4 7 0 1 0 2 3 5 4 1 3 4 1 2 1 1 0 0 0 0 10 0 11 0 12 0 14 0 0 0 3 5 7 WNW NW NNW Variable 0 0 0 0 1 2 5 4 0 0 8 3 0 10 0 13 0 14 2 11 0 0 0 0 0 0 0 Total 0 27 67 39 5 0 138 0 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 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 Winds Measured at 296 Feet Delta-T (F)Wind Speed (in mph)Wind Direction N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 1-3 4-7 8-12 13-18 19-24 > 24 Total 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 6 2 8 1 1 1 4 7 3 10 1 0 4 9 7 14 9 0-____8 7 8 6 4 1 4 6 5 10 5 1 1 1 6 6 0------------------__ _0 15 0 9 0 17 0 9 0 6 0 4 0 9 0 16 0 11 0 28 0 17 0 8 0 1 1 0 1 1 0 22 0 15 0 0 Total 1 96 79 29 3 0 208 Hours of calm in this stability class: Hours of missing wind measurements in this Hours of missing stability measurements in 0 stability class: 0 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 N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 1-3 4-7 1 20 2 9 3 14 3 10 1 3 0 2 0 6 0 9 1 10 0 12 1 10 0 14 1 9 1 15 4 6 1 14 0 0 8-12 13-18 19-24 > 24 16 21 2 0 10 10 0 0 14 10 0 0 13 3 0 0 13 6 0 0 16 15 0 0 10 2 2 0 8 6 0 0 11 12 3 0 15 15 8 0 16 7 3 0 10 15 0 0 2 9 2 0 7 7 3 0 21 12 3 2 13 10 1 1 0 0 0 0 Total 60 31 41 29 23 33 20 23 37 50 37 39 23 33 48 40 0 Total 19 163 195 160 27 3 567 Hours of calm in this stability class: 0 Hours of missing Hours of missing wind measurements in this stability class: 0 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 NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable Total 0 6 20 22 2 6 22 18 0 3 13 16 0 4 22 3 1 6 7 6 0 3 9 17 2 3 15 15 0 3 14 14 0 3 13 26 0 0 9 34 1 3 9 11 1 1 8 5 0 0 12 13 0 2 5 17 0 1 10 21 0 0 7 16 0 0 0 0 0 0 0 0 0 2 0 2 8 1 0 3 3 0 0 2 0 0 30 0 48 0 48 0 32 0 29 0 20 0 31 0 35 0 33 1 51 0 53 0 27 0 18 0 25 0 24 0 34 0 23 0 0 1 531 7 44 195 254 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 Winds Measured at 296 Feet Delta-T (F)Wind Speed (in mph)Wind Direction_________N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 1-3 4-7 8-12 13-18 19-24 > 24 Total_ _ _ ------------------------------4 6 2 6 18 7 4 9 1 3 3 4 4 20 3 4 17 16 2 9 14 3 13 25 0 12 35 2 6 33 2 3 0 2 4 4 0 5 12 0 0 6 1 3 7 2 0 2 0 0 0 0 14 0 31 0 16 0 10 0 28 0 38 0 25 0 43 0 51 0 43 0 6 0 11 0 18 0 7 0 11 0 5 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 N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 4-7 8-12 13-18 19-24 > 24 6 7 0 0 0 0 3 0 0 0 1 4 1 0 0 8 4 2 0 0 4 1 0 0 0 6 10 4 0 0 2 4 11 0 0 3 7 12 0 0 7 16 27 0 0 2 19 16 0 0 1 4 3 0 0 2 1 0 0 0 3 2 1 0 0 1 3 1 0 0 1 4 1 0 0 0 3 2 0 0 0 0 0 0 0 Total 15---15 6 18 7 21 18 22 50 39 9 3 8 6 6 5 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 Direction Wind Speed (in mph)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 0 2 4 2 0 0 2 0 6 1 8 17 2 5 4 4 1 0 1 5 13 5 0 2 2 0 7 33-21 5 9 14 14 6 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 N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 0 0 0 0 0 0 0 0 0 0 0 10 0 0 0 0 0 0 1 0 1 1 0 0 1 0 2 5 2 2 1 0 3 0 0 8-12 13-18 19-24 > 24 0 0 0 0 1 0 0 0 2 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 2 0 0 0 0 0 0 0 1 0 0 0 1 1 0 0 2 3 0 0 2 0 0 0 0 0 0 0 0 0 0 0 Total 1 1 3 1 0 0 2 0 2 7 2 3 3 5 5 0 0 Total 0 19 12 4 0 0 35 Hours of calm in this stability class: Hours of missing wind measurements in this Hours of missing stability measurements in 0 stability class: 0 all stability classes: 0 194 of 206 Quad Cities Nuclear Station Period of Record: October -December2005 Stability (Wind Direction N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable Class -Slightly Unstable Winds Measured at Wind Speed 1-3 4-7 8-12-196Ft-33Ft Delta-T (F)33 Feet (in mph)13-18 19-24 > 24 Total_ _ _ _ _ ---------------_____0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0o 4 1 1 5 3 1 3 3 3 3 8 5 15 6 8 5 0-____7 3 2 0 0 0 1 1 4 0 3 2 5 2 9 0 0 11 4 3 5 3 1 4 4 7 3 11 7 20 8 18 6 0 Total 0 74 39 2 0 0 115 Hours of calm in this stability class: Hours of missing wind measurements in this Hours of missing stability measurements in 0 stability class: 0 all stability classes: 0 195 of 206 Quad Cities Nuclear Station Period of Record: October Stability Class -Neutral Winds Measured at Wind Speed Wind-December2005

-196Ft-33Ft Delta-T (F)33 Feet (in mph)Direction 1-3 4-7 N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable_____7 5 10 9 6 7 5 7 1 4 6 7 11 3 7 3 0-____25 14 26 36 31 18 19 10 21 19 36 56 88 80 57 43 0 8-12 13-18 19-24 > 24 35 1 0 0 4 0 0 0 10 0 0 0 9 0 0 0 13 0 0 0 10 0 0 0 23 2 0 0 6 0 0 0 4 0 0 0 11 0 0 0 22 1 0 0 35 10 0 0 71 30 0 0 62 22 0 0 13 10 0 0 8 0 0 0 0 0 0 0 Total_____68 23 46 54 50 35 49 23 26 34 65 108 200 167 87 54 0 Total 98 579 336 76 0 0 1089 Hours of calm in this stability class: 0 Hours of missing Hours of missing wind measurements in this stability class: 0 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 N 4 NNE 5 NE 10 ENE 8 E 7 ESE 8 SE 13 SSE 12 S 5 SSW 3 SW 7 WSW 10 W 16 WNW 4 NW 7 NNW 3 Variable 0 7 4 19 12 4 7 7 1 8 37 39 32 26 37 25 25 8 0 307 8-12 13-18 19-24 > 24 2 0 0 0 0 0 0 0 2 0 0 0 1 0 0 0 0 1 0 0 10 2 0 0 6 2 0 0 1 0 0 0 5 0 0 0 5 1 0 0 15 1 0 0 2 1 0 0 2 0 0 0 2 0 0 0 0 0 0 0 2 0 0 0 0 0 0 0 Total 13 9 31 21 12 27 28 31 47 48 55 39 55 31 32 13 0 492 0 Total 122 55 8 0 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 N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 1-3 4-7 4 9 10 1 8 12 18 21 6 2 1 2 3 3 3 6 0 0 1 1 3 2 14 3 5 9 4 1 0 6 2 2 0 0 8-12 13-18 19-24 > 24 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Total 4 10 11 4 10 26 21 26 15 6 2 2 9 5 5 6 0 Total 109 53 0 0 0 0 162 0 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 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 Winds Measured at Wind Speed Wind-196Ft-33Ft Delta-T (F)33 Feet (in mph)Direction N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 1-3 4-7 1 0 2 0 6 0 5 0 3 0 25 9 14 1 10 1 3 0 3 0 3 0 1 0 5 0 9 1 5 0 0 0 0 0 8-12 13-18 19-24 > 24 Total-----------------------__ _0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 2 6 5 3 34 15 11 3 3 3 1 5 10 5 0 0 Total 95 12 0 0 0 0 107 Hours of calm in this stability class: Hours of missing wind measurements in this Hours of missing stability measurements in 0 stability class: 0 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 N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 1-3 4-7 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8-12 13-18 19-24 > 24 0 0 0 0 0 0 0 0 0 3 0 0 2 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 0 1 17 6 0 5 0 0 0 1 0 0 0 0 0 0 0 0 3 0 0 2 3 0 0 0 0 0 0 0 0 0 0 Total_____0 0 3 2 0 0 0 0 2 2 4 5 1 0 3 5 0 0 Total 0 0 11 27 7 0 45 Hours of calm in this stability class: Hours of missing wind measurements in this Hours of missing stability measurements in 0 stability class: 0 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 Direction Wind Speed (in mph)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 0 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 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 Winds Measured at 296 Feet Delta-T (F)I Wind Speed (in mph)Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 N 1 6 17 44 8 1 NNE 3 4 11 6 2 0 NE 1 6 12 24 1 0 ENE 3 7 17 24 1 0 E 4 10 28 14 1 0 ESE 3 7 8 8 5 1 SE 3 3 6 16 16 4 SSE 0 7 5 12 12 0 S 2 5 10 14 9 2 SSW 0 7 3 23 17 8 SW 1 7 9 19 11 4 WSW 2 18 28 38 9 7 W 0 12 61 52 34 34 WNW 1 13 38 67 37 23 NW 5 12 24 30 12 14 NNW 4 5 26 33 1 1 Variable 0 0 0 0 0 0 Total 77 26 44 52 57 32 48 36 42 58 51 102 193 179 97 70 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 N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 4-7 8-12 13-18 19-24 > 24 1 5 8 0 0 0 7 2 0 0 6 7 7 7 0 7 9 16 1 0 5 9 4 0 1 2 0 2 5 1 2 5 11 8 1 1 4 4 3 1 2 10 45 11 6 2 4 34 36 7 1 6 22 18 2 0 8 9 4 0 4 13 28 3 0 1 20 15 2 0 0 8 20 3 0 1 6 14 2 0 0 0 0 0 0 Total 14 11 27 33 20 10 27 14 76 84 50 21 49 38 32 24 0 Total 11 35 121 241 103 19 530 Hours of calm in this stability class: Hours of missing wind measurements in this Hours of missing stability measurements in 0 stability class: 5 all stability classes: 1 204 of 206 Quad Cities Nuclear Station Stability Period of Record: October -December2005 Class -Moderately Stable -296Ft-33Ft Winds Measured at 296 Feet Delta-T (F)Wind Speed (in mph)Wind Direction_________N NNE NE 1-3 3 0 1 4-7 8-12 13-18 19-24 > 24 Total_ _ _ _ _ -------------------------1 2 5 3 2 5 0 0 2 0 0 0 0 0 7 4 0 13 ENE 0 6 12 E 1 ESE SE 0 0 4 1 2 0 3 6 2 1 0 1 0 0 0 6 0 0 0 20 6 4 0 15 SSE 0 S 0 SSW SW WSW W WNW 1 0 0 0 0 2 1 1 5 2 3 0 3 15 1 23 6 16 1 5 0 0 0 0 4 7 2 3 2 0 0 3 1 0 22 0 28 0 26 0 0 6 7 0 10 0 8 NW NNW Variable Total 0 0 0 1 2 0 0 12 0 0 3 0 3 0 0 0 16 0 0 5 0 6 38 47 86 20 0 197 Hours of calm in Hours of missing Hours of missing this stability class: wind measurements in this stability measurements in 0 stability class: 8 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 N NNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW Variable 1-3 4-7_____1 0 0 0 1 0 0 1 0 1 1 1 1 0 0 0 0_____0 1 0 2 2 1 0 2 0 0 0 4 3 0 0 2 0 8-12 13-18 19-24 > 24 3 4 0 0 1 0 0 0 3 3 0 0 1 1 0 0 0 0 0 0 0 0 0 0 2 0 1 0 0 1 0 0 1 14 0 0 2 7 1 0 1 2 1 0 1 0 0 0 1 1 0 0 0 2 0 0 1 5 0 0 2 2 0 0 0 0 0 0 Total_____8 2 6 4 3 1 3 4 15 11 5 6 6 2 6 6 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 Hours of missing stability measurements in all sta ty class: bility cl 11 asses: 1 206 of 206

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