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Braidwood, Units 1 and 2 - Transmittal of 2015 Annual Radiological Environmental Operating Report
	ML16132A173
Person / Time
Site:	Braidwood
Issue date:	05/11/2016
From:	Marchionda M; Exelon Generation Co
To:	; Document Control Desk, Office of Nuclear Reactor Regulation
References
	BW160031
	Download: ML16132A173 (252)
	v • d • e

May 11, 2016 BW160031 U.S. Nuclear Regulatory Commission Attn: Document Control Desk Washington, D.C. 20555-0001

Subject:

Braidwood Station, Units 1 and 2 Renewed Facility Operating License Nos. NPF-72 and NPF-77 NRC Docket Nos. STN 50-456 and STN 50-457 2015 Annual Radiological Environmental Operating Report Attached is the 2015 Annual Radiological Environmental Operating Report for Braidwood Station. This report is being submitted in accordance with Technical Specification 5.6.2, "Annual Radiological Environmental Operating Report." This report contains information associated with the station's radiological environmental and meteorological monitoring programs.

This information is consistent with the objectives described in the Offsite Dose Calculation Manual and 10 CFR 50, Appendix I, "Numerical Guides for Design Objectives and Limiting Conditions for Operation to Meet the Criterion

'As Low as is Reasonably Achievable' for Radioactive Material In Light-Water-Cooled Nuclear Power Reactor Effluents," Sections IV.B.2, IV.B.3, and IV.C. Technical Specification

5.6.2 requires

the Annual Radiological Environmental Operating Report to be submitted by May 15 of each year. If you have any questions regarding this information, please contact Steven Reynolds, Regulatory Assurance Manager, at (815) 417-2800.

Respectfully, /hffe0 Marri Marchionda Site Vice President Braidwood Station cc: US NRC Regional Administrator, Region Ill US NRC Senior Resident Inspector

-Braidwood Station NRR Project Manager -Braidwood Station Illinois Emergency Management Agency-Division of Nuclear Safety BRAIDWOOD STATION UNITS 1 and 2 Annual Radiological Environmental Operating Report

1 January through 31 December 2015 Prepared By May 2016 Braidwood Station Braceville, IL 60407 Docket No:

50-457 50-456 Teledyne Brown Engineering Environmental Services

Intentionally left blank i Table Of Contents I. Summary and Conclusions

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1 II. Introduction

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3 A. Objectives of the REMP

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3 B. Implementation of the Objectives

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........ 3 III. Program Description

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...... 3 A. Sample Collection

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3 B. Sample Analysis

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.. 6 C. Data Interpretation

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6 D. Program Exceptions

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7 E. Program Changes

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11 IV. Results and Discussion

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11 A. Aquatic Environment

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11 1. Surface Water

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11 2. Public Water

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12 3. Ground/Well Water

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12 4. Fish ................................

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......... 13 5. Sediment

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. 13 B. Atmospheric Environment

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14 1. Airborne ................................

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.. 14 a. Air Particulates

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14 b. Airborne Iodine

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15 C. Terrestrial Environment

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15 1. Milk ................................

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15 2. Food Products

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15 D. Ambient Gamma Radiation

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16 E. Land Use Survey

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16 F. Errata Data

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........ 17 G. Summary of Results

- Inter-laboratory Comparison Program

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17 ii Appendices Appendix A Radiological Environmental Monitoring Report Annual Summary Tables Table A-1 Radiological Environmental Monitoring Program Annual Summary for Braidwood Station, 201 5 Appendix B Location Designation, Distance & Direction, and Sample Collection & Analytical Methods Tables Table B-1 Radiological Environmental Monitoring Program

- Sampling Locations, Distance and Direction, Braidwood Station, 201 5 Table B-2 Radiological Environmental Monitoring Program

- Summary of Sample Collection and Analytical Methods, Braidwood Station, 201 5 Figures Figure B-1 Inner Ring OSLD Locations of the Braidwood Station, 201 5 Figure B-2 Fixed Air Sampling and Outer Ring OSLD Locations of the Braidwood Station, 201 5 Figure B-3 Ingestion and Waterborne Exposure Pathway Sample Locations of the Braidwood Station, 201 5 Appendix C Data Tables and Figures

- Primary Laboratory Tables Table C-I.1 Concentrations of Gross Beta in Surface Water Samples Collected in the Vicinity of Braidwood Station, 201 5. Table C-I.2 Concentrations of Tritium in Surface Water Samples Collected in the Vicinity of Braidwood Station, 201 5. Table C-I.3 Concentrations of Nickel-63 in Surface Water Samples Collected in the Vicinity of Braidwood Station, 201 5. Table C-I.4 Concentrations of Gamma Emitters in Surface Water Samples Collected in the Vicinity of Braidwood Station, 201 5. Table C-II.1 Concentrations of Gross Beta in Public Water Samples Collected in the Vicinity of Braidwood Station, 201 5.

iii Table C-II.2 Concentrations of Tritium in Public Water Samples Collected in the Vicinity of Braidwood Station, 201 5. Table C-II.3 Concentrations of I

-131 in Public Water Samples Collected in the Vicinity of Braidwood Station, 201 5. Table C-II.4 Concentrations of Gamma Emitters in Public Water Samples Collected in the Vicinity of Braidwood Station, 201 5. Table C-III.1 Concentrations of Tritium in Ground/

Well Water Samples Collected in the Vicinity of Braidwood Station, 201 5. Table C-III.2 Concentrat ions of Gamma Emitters in Ground/Well Water Samples Collected in the Vicinity of Braidwood Station, 201 5. Table C-IV.1 Concentrations of Nickel-63 and Gamma Emitters in Fish Samples Collected in the Vicinity of Braidwood Station, 201 5. Table C-V.1 Concentrations of Nickel-63 and Gamma Emitters in Sediment Samples Collected in the Vicinity of Braidwood Station, 201 5. Table C-VI.1 Concentrations of Gross Beta in Air Particulate Samples Collected in the Vicinity of Braidwood Station, 201 5. Table C-VI.2 Monthly and Yearly Mean Values of Gross Beta Concentrations in Air Particulate Samples Collected in the Vicinity of Braidwood Station, 201 5. Table C-VI.3 Concentrations of Gamma Emitters in Air Particulate Samples Collected in the Vicinity of Braidwood Station, 2 01 5. Table C-VII.1 Concentrations of I

-131 in Air Iodine Samples Collected in the Vicinity of Braidwood Station, 201 5. Table C-VIII.1 Concentrations of I

-131 in Milk Samples Collected in the Vicinity of Braidwood Station, 201 5. Table C-VIII.2 Concentrations of Gamma Emitters in Milk Samples Collected in the Vicinity of Braidwood Station, 201 5. Table C-IX.1 Concentrations of Gamma Emitters in Vegetation Samples Collected in the Vicinity of Braidwood Station, 201 5. Table C-X.1 Quarterly OSLD Results for Braidwood Station, 201 5. Table C-X.2 Mean Quarterly OSLD Results for the Inner Ring, Outer Ring, Other, Control, and Independent Spent Fuel Storage Installation (ISFSI)

Locations for Braidwood Station, 201 5. Table C-X.3 Summary of the Ambient Dosimetry Program for Braidwood Station, 201 5. Figures Figure C-1 Surface Water

- Gross Beta

- Stations BD

-10 and BD-25 (C) Collected in the Vicinity of Braidwood Station, 2000

- 201 5.

iv Figure C-2 Surface Water

- Gross Beta

- Stations BD

-38 and BD-40 Collected in the Vicinity of Braidwood Station, 200 7 - 201 5. Figure C-3 Surface Water

- Gross Beta

- Stations BD

-55 and BD-56 Collected in the Vicinity of Braidwood Station, 2007 - 201 5. Figure C-4 Surface Water

- Tritium - Stations BD

-10 and BD-25 (C) Collected in the Vicinity of Braidwood Station, 2000

- 201 5. Figure C-5 Surface Water

- Tritium - Stations BD

-38 and BD-40 Collected in the Vicinity of Braidwood Station, 200 6 - 201 5. Figure C-6 Surface Water

- Tritium - Stations BD

-55 and BD-56 Collected in the Vicinity of Braidwood Station, 2007 - 201 5. Figure C-7 Public Water

- Gross Beta

- Station BD

-22 Collected in the Vicinity of Braidwood Station, 2000

- 201 5. Figure C-8 Public Water

- Tritium - Station BD

-22 Collected in the Vicinity of Braidwood Station, 2000

- 201 5. Figure C-9 Ground/Well Water

- Tritium - Stations BD

-13 and BD-34 Collected in the Vicinity of Braidwood Station, 2000

- 201 5. Figure C-10 Ground/Well Water

- Tritium - Stations BD

-35 and BD-36 Collected in the Vicinity of Braidwood Station, 2000

- 201 5. Figure C-11 Ground/Well Water

- Tritium - Station BD

-37 Collected in the Vicinity of Braidwood Station, 2000

- 201 5. Figure C-12 Ground/Well Water

- Tritium - Stations BD

-50 and BD-51 Collected in the Vicinity of Braidwood Station, 2007 - 201 5. Figure C-13 Gr ound/Well Water

- Tritium - Stations BD

-53 and BD-54 Collected in the Vicinity of Braidwood Station, 2007 - 201 5. Figure C-14 Air Particulate

- Gross Beta

- Stations BD

-03 (C) and BD

-06 Collected in the Vicinity of Braidwood Station, 2000

- 201 5. Figure C-15 Air Particulate

- Gross Beta

- Stations BD

-19 and BD-20 Collected in the Vicinity of Braidwood Station, 2000

- 201 5. Figure C-16 Air Particulate

- Gross Beta

- Station BD

-21 Collected in the Vicinity of Braidwood Station, 2000

- 201 5. Figure C-17 Air Particulate

- Gross Beta

- Station s BD-02 and BD-04 Collected in the Vicinity of Braidwood Station, 2005 - 201 5. Figure C-18 Air Particulate

- Gross Beta

- Station BD

-05 Collected in the Vicinity of Braidwood Station, 2005 - 201 5.

v Appendix D Inter-Laboratory Comparison Program Tables Table D-1 Analytics Environmental Radioactivity Cross Check Program Teledyne Brown Engineering, 201 5 Table D-2 ERA Environmental Radioactivity Cross Check Program Teledyne Brown Engineering, 201 5 Table D-3 DOE's Mixed Analyte Performance Evaluation Program (MAPEP)

Teledyne Brown Engineering, 201 5 Table D-4 ERA Statistical Summary Proficiency Testing Program for Environmental, Inc., 201 5 Table D-5 DOE's Mixed Analyte Performance Evaluation Program (MAPEP)

Environmental, Inc., 201 5 Appendix E Effluent Data

Appendix F Meteorological Data

Appendix G Errata Data

Appendix H Annual Radiological Groundwater Protection Program Report (ARGPPR) 1 I. Summary and Conclusions This report on the Radiological Environmental Monitoring Program (REMP) conducted for Exelon's Braidwood Station covers the period January 1, 201 5 through December 31, 201 5. During that time period 1, 645 analyses were performed on 1

, 3 33 samples. In assessing all the data gathered for this report and comparing these results with preoperational data, it was concluded that the operation of Braidwood Station had no adverse radiological impact on the environment.

Surface, public, and ground/well water samples were analyzed for concentrations of tritium and gamma emitting nuclides. Surface water and public water samples were also analyzed for concentrations of gross beta. Gross beta and tritium activities detected were consistent with those detected in previous years. No fission or activation products were detected. As part of an effort to implement industry best practices, both gaseous and liquid station effluents were evaluated for all 10CFR61 required nuclides. Nuclides exceeding 1% relative abundance in the waste stream were added to the list of nuclides that Teledyne Brown evaluates in potentially impacted REMP matrices. For Braidwood Station, Ni-63 exceeds 1% relative abundance in the radwaste resins. Occasionally, Ni-63 is observed in liquid release tank quarterly composites, therefore, beginning in the fall of 2013 the station requested that Ni

-63 be evaluated in the downstream surface water, sediment, and fish analyses. Ni

-63 has not been observed in downstream surface water.

Fish (commercially and/or recreationally important species) and sediment samples were analyzed for concentrations of gamma emitting nuclides.

No fission or activation products were detected in fish. Nickel-63 was not detected in any fish or sediment samples analyzed.

T wo sediment sample s had Cs-137. The concentration was consistent with levels observed during the preoperational years. No plant produced fission or activation products 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 I

-131 analyses were performed on weekly air samples. All results were less than the minimum detectable concentration for I

-131. Cow milk samples were analyzed for concentrations of I-131 and gamma emitting nuclides.

Iodine-131 was not detected in any milk sample s. Concentrations of naturally occurring K

-40 were detected. No fission or activation products were found and all required LLDs (Lower Limit of Detection) were met. Food Product samples were analyzed for concentrations of gamma emitting nuclides. No plant produced fission or activation products were detected.

Environmental gamma radiation measurements were performed quarterly using 2 Optically Stimulated Luminescence D osimeters (OS LD). Beginning in 2012 , Exelon changed the type of dosimetry used for the Radiological Environmental Monitoring Program (REMP). Optically Stimulated Luminescent Dosimetry were deployed and Thermo

-luminescent Dosimetry (TLD) were discontinued.

This change may result in a step change in readings , up or down, depending on site characteristics. The relative comparison to control locations remains valid.

OSLD technology is different than that used in a TLD but has the same purpose (to measure direct radiation

).

II. Introduction The Braidwood Station, consisting of two 3

, 58 7 MWt pressurized water reactors owned and operated by Exelon Corporation is located in Will County, Illinois. Unit No. 1 went critical on May 29, 1987. Unit No. 2 went critical on March 08, 1988. The site is located in northeastern Illinois, 15 miles south

-southwest of Joliet, Illinois, 60 miles southwest of Chicago and southwest of the Kankakee River.

This report covers those analyses performed by Teledyne Brown Engineering (TBE), Landauer Technologies and Environmental Inc. (Midwest Labs) on samples collected during the period January 1, 201 5 through December 31, 201 5.

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.

III. Program Description A. Sample Collection Samples for the Braidwood Station REMP were collected for Exelon Nuclear by Environmental Inc. (Midwest Labs). This section describes the general collection methods used by Environmental Inc. (Midwest Labs) to obtain environmental samples for the Braidwood Station REMP in 201 5. Sample locations and descriptions can be found in Table B

-1 and Figures B-1 through B

-3, Appendix B. The sampling methods used by Environmental Inc. are listed in Table B

-2. Aquatic Environment The aquatic environment was evaluated by performing radiological analyses on samples of surface water, public water, well water, fish, and sediment. Two gallon water samples were collected weekly from six surface water locations (BD

-10, BD-25 [control], BD

-38, BD-40, BD-55 and BD-56), and one weekly composite sample s of public drinking water at location (BD

-22) and ground/well water samples collected quarterly from eight locations (BD

-13, BD-34, BD-35, BD-36, BD-37, BD-50, BD-51 and BD-54). All samples were collected in new unused plastic bottles, which were rinsed with source water prior to collection. Fish samples comprising the flesh of largemouth bass, golden redhorse , freshwater drum, smallmouth bass , and common carp were collected semiannually at three locations, BD

-25 (control), BD

-28 and BD-41. Sediment samples composed of recently deposited substrate were collected at three locations semiannually, BD

-10, BD-25 (control), and BD-57. Atmospheric Environment The atmospheric environment was evaluated by performing radiological analyses on samples of air particulate and airborne iodine.

Air particulate samples were collected and analyzed weekly at eight locations (BD

-02, BD-03, BD-04, BD-05, BD-06, BD-19, BD-20 and BD-21). The control location was BD

-03. 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 filters and air iodine samples were replaced weekly and sent to the laboratory for analysis.

Terrestrial Environment

The terrestrial environment was evaluated by performing radiological analyses on milk and food product samples. Milk samples were collected biweekly at one location (BD

-17) from Ma y through October and monthly from November through April. Control location (BD

-18) was missed twice (January 2015 and December 2015) but milk was available for the rest of 2015. All samples were collected in new unused two gallon plastic bottles from the bulk tank at each location, preserved with sodium bisulfite and shipped promptly to the laboratory. Food products were collected annually in September at five locations (BD

-Control , BD-Quad 1, BD-Quad 2, BD

-Quad 3 and BD-Quad 4). The control location was BD-Control. Food products were unavailable for collection in September 2015 for locations BD

-Quad 1, BD

-Q uad 3 and BD-Quad 4. Various types of samples were collected and placed in new unused plastic bags and sent to the laboratory for analysis.

Ambient Gamma Radiation Beginning in 201 2, Exelon changed the type of dosimetry used for the Radiological Environmental Monitoring Program (REMP).

Optically

Stimulated Luminescent Dosimeters (OSLD) were deployed and the use of Thermoluminescent Dosimeters (TLD) w as discontinued. This change may result in a step change in readings , up or down, depending on site characteristics. The relative comparison to control locations remains valid. OSLD technology is different than that used in a TLD but has the same purpose (to measure direct radiation

).

Each location consisted of 2 OSLD s. The OSLDs were exchanged quarterly and sent to Landauer for analysis. The OSLDs were placed at locations on and around the Braidwood Station site as follows:

An inner ring consisting of 16 locations (BD

-101, BD-102, BD-103, BD-104, BD-105, BD-106, BD-107, BD-108, BD-109, BD-110, BD-111a, BD-112, BD-113a, BD-114, BD-115 and BD

-116) at or near the site boundary.

An outer ring consisting of 16 locations (BD

-201, BD-202, BD-203, BD-204, BD-205, BD-206, BD-207, BD-208, BD-209, BD-210, BD-211, BD-212, BD-213, BD-214, BD-215 and BD-216) extending to approximately 5 miles from the site.

An additional (other) set consisting of seven locations (BD

-02, BD-04, BD-05, BD-06, BD-19, BD-20 and BD-21).

The balance of one location (BD

-03) represent s the control area.

The specific OSLD 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

3. where estimated annual dose from Braidwood Station, if any , would be most significant.

B. Sample Analysis This section describes the general analytical methodologies used by TBE and Environmental Inc. (Midwest Labs) to analyze the environmental samples for radioactivity for the Braidwood Station REMP in 201 5. 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 public and surface water and air particulates.

2. Concentrations of gamma emitters in public, ground/well and surface water, air particulates, milk, fish, sediment and food products. 3. Concentrations of tritium in public, ground/well and surface water.

4. Concentrations of I

-131 in air , mi lk and public water. 5. Concentrations of Ni

-63 in surface water, fish and sediment

. 6. Ambient gamma radiation levels at various site environs.

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

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

The MDC is the smallest concentration of radioactive material in a sample that will yield a net count, above system background, that will be detected with 95% probability with only 5% probability of falsely concluding that a blank observation represents a "real" signal. The MDC is an a postori determination.

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 resulting in 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, ground/well water

, and fish 12 nuclides, Mn

-54, Co-58, Fe-59, Co-60, Zn-65, Nb-95, Zr-95 , I-131, Cs-134, Cs-137, Ba-140 and La-140 were reported.

For public water, sediment, air particulate, milk and vegetatio n 11 nuclides, Mn

-54, Co-58, Fe-59, Co-60, Zn-65, Nb-95, Zr-95, Cs-134, Cs-137, Ba-140 and 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 the single analysis uncertainty.

D. Program Exceptions For 20 1 5 the Braidwood Station REMP had a sample recovery rate in excess of 9 8.3%. Sample anomalies and missed samples are listed in the tables below:

Table D-1 LISTING OF SAMPLE ANOMALIES Sample Location Collection Reason Type Code Date WW BD-34, BD-35, 01/08/15 No sample; homeowners absent; BD-36, BD-37, BD-50 water shut off. Samples collected.

01/15/15. WW BD-54 01/08/15 No sample; valve frozen. Sample collected 01/15/15.

MI BD-17 01/0 8/1 5 No milk available. Sample collected 01/15/15.

A/I BD-2 1 0 2/05/1 5 No access; road not plowed. POC notified; will collect next week

.

OSLD BD-21 02/05/1 5 No access; road not plowed. Sample collected 02/12/15

.

A/I BD-0 2 0 3/0 5/1 5 No apparent reason for the low reading of 1 63.2 hours2.314815e-5 days 5.555556e-4 hours 3.306878e-6 weeks 7.61e-7 months . A/I BD-21 0 4/30/1 5 Regulator malfunction; pump removed for repair. Flowrate = 72 cfh. Flow of new pump (60 cfh) use d for COC.

A/I All samplers 06/2 5/1 5 Low reading at all samplers due to storm/tornado

.

A/I BD-0 3 0 7/2 3/1 5 Low reading of 150.7 hours8.101852e-5 days 0.00194 hours 1.157407e-5 weeks 2.6635e-6 months due to tripped circuit breaker

.

A/I BD-03 07/30/1 5 Low reading of 25.7 hours8.101852e-5 days 0.00194 hours 1.157407e-5 weeks 2.6635e-6 months due to tripped circuit breaker

. A/I BD-0 3 0 9/17/1 5 Timer malfunction; collector replaced timer. Estimated time @ 167.1 hours1.157407e-5 days 2.777778e-4 hours 1.653439e-6 weeks 3.805e-7 months based on previous weeks' time

. A/I BD-0 5 1 0/22/1 5 Timer malfunction; collector replaced timer. Estimated time @ 168.0 hours0 days 0 hours 0 weeks 0 months based on previous weeks' time

.

Table D-1 LISTING OF SAMPLE ANOMALIES (continued)

Sample Location Collection Reason Type Code Date A/I BD-19 1 1/2 5/15 Low reading of 46.3 hours3.472222e-5 days 8.333333e-4 hours 4.960317e-6 weeks 1.1415e-6 months due to recent power restoration

. A/I BD-19 1 2/03/15 Low vacuum of 8mHg; collector replaced pump. PW BD-22 1 2/2 4/15 Unable to collect sample; new lock on utility building; no key available. New key obtained by station on 12/28/15l Sample collected 12/29/15 @ 07:45. Table D-2 LISTING OF MISSED SAMPLES Sample Location Collection Reason Type Code Date MI BD-18 01/08/15 Farmer sold cows in 2014; milk not available until 02/01/15

.

SW BD-38, BD-55, 01/0 8/15 No sample; water frozen.

BD-56 SW BD-38, BD-55, 01/15/15 No sample; water frozen.

BD-56 SW BD-38, BD-55, 01/22/15 No sample; water frozen.

BD-56 SW BD-55, BD-56, 01/29/15 No sample; water frozen.

SW BD-38, BD-55, 0 2/05/1 5 No sample; water frozen.

BD-56 SW BD-38, BD-55, 0 2/12/1 5 No sample; water frozen.

BD-56 SW BD-38, BD-55, 0 2/19/1 5 No sample; water frozen.

BD-56 SW BD-38, BD-55, 0 2/2 6/1 5 No sample; water frozen.

BD-56 Table D-2 LISTING OF MISSED SAMPLES (continued)

Sample Location Collection Reason Type Code Date SW BD-25, BD-38 , 0 3/05/1 5 No sample; water frozen.

BD-55, BD-56 SW BD-55, BD-5 6 , 0 3/12/1 5 No sample; water frozen.

OSLD BD-21 0-2 0 7/0 2/15 OSLD found missing during quarterly exchange; collector placed new 3 rd quarter OSLD

.

OSLD BD-201-1 09/01/15 OSLD found missing during monthly visual check; collector placed spare 291551 00133 8619.

OSLD BD-201-2 09/01/15 OSLD found missing during monthly visual check; collector placed spare 291551 00134 8620.

VE BD-Quad 1, 3, 4 09/23/15 After diligent search of quadrants, no root or broad leaf vegetation locat ed.

A/I BD-19 11/19/15 No power to sampler; POC notified.

M BD-18 1 2/0 3/1 5 No sample available; farmer not milking at this time

. Air samples collected between the period of 08/27/15 through 09/03/15 at all locations BD

-02, BD-03, BD-04, BD-05, BD-06, BD-19, BD-20, and BD-21 measured slightly elevated levels of gross beta. This is due to higher levels of dust in the air as a result of crop harvesting as expected at this time of year. The air sampler filter papers were observed to be darker than normal with a very heavy material deposition. Darker filter papers and similar results were also seen at other nearby Stations during the same time period.

Each program exception was reviewed to understand the causes of the program exception. Sampling and maintenance issues were reviewed with the personnel involved to prevent recurrence. Occasional equipment breakdowns

, power outages and weather related issues were unavoidable.

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

E. Program Changes There were no program changes in 201

5.

IV. Results and Discussion A. Aquatic Environment

1. Surface Water

Samples were taken weekly and composited monthly at six locations (BD

-10, BD-25 (control), BD-38, BD-40, BD-55 and BD-56). Of these locations

, only BD-10 could be affected by Braidwood Station's effluent releases as it is downstream of the NPDES permitted outfall. The following analyses were performed.

Gross Beta

Samples from all locations were analyzed for concentrations of gross beta (Table C-I.1, Appendix C). Gross beta was detected in 59 of 6 7 samples. The values ranged from 2.

3 to 1 2.7 pCi/L. Concentrations detected were consistent with those detected in

previous years (Figures C

-1 through C

-3, Appendix C).

Tritium Quarterly composites of weekly collections were analyzed for tritium activity (Table C

-I.2, Appendix C).

Tritium activity was detected in one sample. The value was 267 pCi/l (Figures C

-4 through C-6, Appendix C)

. Nickel-63 Monthly samples were analyzed for Nickel

-63 activity (Table C

-I.3, Appendix C).

Nickel-63 was not detected and the required LLD was met. Gamma Spectrometry

Samples from all locations were analyzed for gamma emitting nuclides (Table C

-I.4, Appendix C). No nuclides were detected and all required LLDs were met.

2. Public Water Monthly composite s of weekly samples were made at one location (BD-22). This location could be affected by Braidwood Station's effluent releases. The following analyses were performed:

Gross Beta Samples from the location were analyzed for concentrations of gross beta (Tables C

-II.1, Appendix C). Gross beta was detected in 1 0 of 12 samples. The values ranged from 2.3 to 6.4 pCi/L. Concentrations detected were consistent with those detected in previous years (Figure C

-7, Appendix C).

Tritium Monthly composites of weekly samples from BD

-22 were analyzed for tritium activity (Table C

-II.2, Appendix C). Tritium was detected in nine of 12 samples. The concentration ranged from 2 2 0 to 572 pCi/L. Concentrations detected were consistent with those detected in previous years (Figure C

-8, Appendix C)

. Iodine Monthly composites of weekly samples from the location were analyzed for I

-131 (Table C-II.3, Appendix C). Iodine was not detected in any samples and the required LLD was met

. Gamma Spectrometry

Samples from the location were analyzed for gamma emitting nuclides (Table C

-II.4, Appendix C). No nuclides were detected and all required LLDs were met.

3. Ground/Well Water Quarterly samples were collected a t eight locations (BD

-13, BD-34, BD-35, BD-36, BD-37, BD-50, BD-51and BD-54). The following analyses were performed:

Tritium Quarterly grab samples from the locations were analyzed for tritium activity (Table C

-III.1, Appendix C). Tritium was not detected in any sample and the required LLD was met.

(Figures C

-9 through C-13, Appendix C)

. Gamma Spectrometry

Samples from all locations were analyzed for gamma emitting nuclides (Table C

-III.2, Appendix C). No nuclides were detected and all required LLDs were met.

4. Fish Fish samples comprised of largemouth bass, golden redhorse ,

freshwater drum , smallmouth bass, common carp, and largemouth bass were collected at three locations (BD

-25, BD-28, and BD

-41) semiannually. Location BD

-28 could be affected by Braidwood Station's effluent releases. The following analysis was performed:

Gamma Spectrometry

The edible portion of fish samples from all three locations was analyzed for gamma emitting nuclides (Table C

-IV.1, Appendix C). No fission or activation products were found. No nuclides were detected and all required LLDs were met.

5. Sediment Aquatic sediment samples were collected at three locations (BD-10, BD-25, and BD-57) semiannually. The locations at the Braidwood Station outfall to the Kanakakee River and downstream of the outfall, could be affected by Braidwood Station's effluent releases. The following analysis was performed:

Gamma Spectrometry Sediment samples from the location were analyzed for gamma emitting nuclides (Table C

-V.1, Appendix C). Concentrations of the fission product Cs

-137 were found at location s BD-10 and BD-57. The concentration ranged from 1 4 2 to 1 6 8 pCi/kg dry. The concentrations of Cs

-137 at locations BD

-10 and BD-57 were less than the required Cs

-137 in sediment LLD of 180 pCi/kg dry. The activity detected was consistent with those detected in previous years (29 pCi/kg to 260 pCi/kg from 1995 to 2006). No other

Braidwood fission or activation products were found and all

required LLDs were met.

B. Atmospheric Environment

1. Airborne a. Air Particulates Continuous air particulate samples were collected from eight locations on a weekly basis. The eight locations were separated into three groups: Near field samplers (BD

-06, BD-19, BD-20 and BD-21), far field samplers within 10 km of the site (BD

-02, BD-04 and BD-05) and the Control sampler between 10 and 30 km from the site (BD

-03). The following analyses were performed:

Gross Beta Weekly samples were analyzed for concentrations of beta emitters (Table C

-VI.1 and C

-VI.2, Appendix C).

Detectable gross beta activity was observed at all locations.

Comparison of results among the three groups aid in determining the effects, if any, resulting from the operation of Braidwood Station. The results from the near field (Group I) ranged from 5 E-03 to 3 8 E-02 pCi/m 3 with a mean of 1 7 E-02 pCi/m 3. The results from the far field (Group II) range d from 5 E-03 t o 4 3 E-02 pCi/m 3 with a mean of 1 7 E-02 pCi/m 3. The results from the Control location (Group III) ranged from 6 E-03 to 32 E-02 pCi/m 3 with a mean of 1 7 E-02 pCi/m 3. Comparison of the 201 5 air particulate data with previous years data indicate no effects from the operation of Braidwood Station. In addition a comparison of the weekly mean values for 201 5 indicate no notable differences among the three groups (Figures C

-14 through C-18, Appendix C). Gamma Spectrometry

Weekly samples were composited quarterly and analyzed for gamma emitting nuclides (Table C

-VI.3, Appendix C). No nuclides were detected and all required LLDs were met.

b. Airborne Iodine Continuous air samples were collected from eight location s (BD-02, BD-03, BD-04, BD-05, BD-06, BD-19, BD-20 and BD-21) and analyzed weekly for I

-131 (Table C

-VII.1, Appendix C). All results were less than the minimum detectable concentration for I

-131. C. Terrestrial Environment

1. Milk Samples were collected from two location s (BD-17 and control location BD

-18). Sampling frequencies were increased to biweekly in Ma y and continued through October and monthly sampling was performed November through Apri l. The following analyses were performed:

Iodine-131 Milk samples from the indicator location were analyzed for concentrations of I

-131 (Table C

-VIII.1, Appendix C).

Iodine-131 was not detected in any sample s. All required LLDs were met.

Gamma Spectrometry Each milk sample was analyzed for concentrations of gamma emitting nuclides (Table C

-VIII.2, Appendix C). No nuclides were detected and all required LLDs were met. 2. Food Products Food product samples were collected at five locations (BD

-Control, BD

-Quad 1, BD

-Quad 2, BD

-Quad 3 and BD

-Quad 4) when available. Four locations, (located downwind, BD-Quad 1, BD

-Quad 2, BD

-Quad 3 and BD

-Quad 4) could be affected by Braidwood Station's effluent releases. Food products were unavailable for collection in September 2015 for locations BD

-Quad 1, BD

-Q uad 3 and BD-Quad 4. The following analysis was performed:

Gamma Spectrometry Samples from all locations were analyzed for gamma emitting nuclides (Table C

-IX.1, Appendix C).

No nuclides were detected and all required LLDs were met. D. Ambient Gamma Radiation

Ambient gamma radiation levels were measured utilizing Optically Stimulated Luminescence Dosimeter (OSLD). Eighty Six OSLD locations were established around the site. Results of OSLD measurements are listed in Tables C

-X.1 to C-X.3, Appendix C.

Most OSLD measurements were below 3 0 mrem/quarter, with a range of 13.8 to 3 1.3 mrem/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 locations were similar.

E. Land Use Survey

A Land Use Survey conducted during August 20 1 5 around the Braidwood Station was performed by Environmental Inc. (Midwest Labs) for Exelon Nuclear to comply with section 12.5.2 of the Braidwood Station's Offsite Dose Calculation Manual. The purpose of the survey was to document the nearest resident, milk producing animal and garden of greater than 500 ft 2 in each of the sixteen 22 1/2 degree sectors around the site. For dose calculation, a garden is assumed at the nearest residence. There were no changes required to the Braidwood Station REMP, as a result of this survey. The results of this survey are summarized below.

Distance in Miles from the Braidwood Station Reactor Buildings Sector Residence Miles Livestock Miles Milk Farm Miles (A) N 0.5 2.6 - (B) NNE 0.9 - - (C) NE 0.7 0.9 - (D) ENE 0.8 3.3 - (E) E 1.5 2.3 - (F) ESE 2.2 2.3 - (G) SE 2.7 2.7 - (H) SSE 4.5 - - (J) S 4.2 4.8 - (K) SSW 1.3 5.3 5.5 (L) SW 0.4 1.2 - (M) WSW 0.5 - - (N) W 0.4 1.6 8.7 (P) WNW 0.4 - - (Q) NW 0.4 - - (R) NNW 0.4 - - Distance in Miles from the Braidwood Station ISFSI PAD, 2015 Sector Residence Miles (N) W 0.7 (P) W N W 0.7 (Q) N W 0.7 (R) N N W 0.7 F. Errata Data

1. More accurate distances to the ISFSI pad were updated in the ODCM in 2015

. The distances reported in the 2014 AREOR were incorrect. The distances to ISFSI OSLD dosimeters are included on page B-3. Exact distances for each location are included in Appendix G

- Errata Data. 2. Page B-6, Figure B

-1, Inner Ring and Other map, was updated to reflect the corrected distances there were included in the 2015 ODCM revision.

A. 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 matrice s (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 = "N"). 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 TBE laboratory , 1 29 out of 139 analyses performed met the specified acceptance criteria. Ten analyses (AP

- Cr-51, U-234/233, Gr A, Sr-90; Soil Sr

-90; Water

- Ni-3, Sr-89, Sr-90, U natural; Vegetation Sr

-90 samples) did not meet the specified acceptance criteria for the following reason s: Note: The Department of Energy (DOE) Mixed Analyte Performance Evaluation Program (MAPEP) samples are created to mimic conditions found at DOE sites which do not resemble typical environmental samples obtained at commercial nuclear power facilities.

1. Teledyne Brown Engineering's Analytics' June 2015 air particulate

Cr-51 result of 323 +/- 45.5 pCi was higher than the known value of 233 pCi with a ratio of 1.39. The upper ratio of 1.

3 0 (acceptable with warning) was exceeded. The air particulate sample is counted at a distance above the surface of the detector to avoid detector summing which could alter the results. Chromium

-51 has t he shortest half

-life (27.7 days) and the lowest gamma energy (320.08 keV) of this mixed nuclide sample. Additionally, Cr

-51 has only one gamma energy and also has a low intensity (9.38 gamma photons produced per 100 disintegrations). This geometry produces a larger error for the Cr

-51 and other gamma emitters as any distance from the detector decreases the counting rate and the probability of accurately detecting the nuclide energy. Taking into consideration the uncertainty, the activity of Cr

-51 overlaps with the known value at a ratio of 1.19, which would statistically be considered acceptable. NCR 15

-18 2. Teledyne Brown Engineering's MAPEP March 2015 soil Sr

-90 result of 286 Total Bq/kg was lower than the known value of 653 Bq/kg, exceeding the lower acceptance range of 487 Bq/kg. The failure was due to incomplete digestion of the sample. Incomplete digestion of samples causes some of the sample to be left behind and is not present in the digested sample utilized for analysis. The procedure has been update d to include a more robust digestion using stirring during the heating phase. The MAPEP September 2014 soil Sr

-90 series prior to this study was evaluated as acceptable with a result of 694 and an acceptance range of 601

- 1115 Bq/kg. The MAPEP September 2015 series soil Sr-90 after this study was evaluated as acceptable with a result of 429 and an acceptance range of 298

- 553 Bq/kg. We feel the issue is specific to the March 2015 MAPEP sample. NCR 15-13 3. Teledyne Brown Engineering's MAPEP March 2015 air particulate U-234/233 result of 0.0211 +/- 0.0120 Bq/sample was higher than the known value of 0.0155 Bq/sample, exceeding the upper acceptance range of 0.0202 Bq/sample. Although evaluated as a failure, taking into consideration the uncertainty, TBE's result would overlap with the known value, which is statistically considered acceptable. MAPEP spiked the sample with significantly more

U-238 activity (a found to known ratio of 0.96) than the normal U-234/233. Due to the extremely low activity, it was difficult to quantify the U

-234/233. NCR 15

-13

4. Teledyne Brown Engineering's MAPEP March 2015 air particulate gross alpha result of 0.448 Bq/sample was lower than the known value of 1.77 Bq/sample, exceeding the lower acceptance range of 0.53 Bq/sample. The instrument efficiency used for gross alpha is determined using a non

-attenuated alpha standard. The MAPEP filter has the alphas embedded in the filter, requiring an attenuated efficiency. When samples contain alpha particles that are embedded in the sample media, due to the size of the alpha particle, some of the alpha particles are absorbed by the media and

cannot escape to be counted. When the sample media absorbs the alpha particles this is known as self

-absorption or attenuation. The calibration must include a similar configuration/media to correct for the attenuation. In order to correct the low bias, TBE will create an attenuated efficiency for MAPEP air particulate filters.

The MAPEP September series air particulate gross alpha result of 0.47 Bq/sample was evaluated as acceptable with a range of 0.24

- 1.53 Bq/sample. Unlike the MAPEP samples, air particulate Gross alpha analyses for power plants are not evaluated as a direct count sample. Power plant air particulate filters for gross alpha go through an acid digestion process prior to counting and the digested material is analyzed. NCR 15-13 5. Teledyne Brown Engineering's MAPEP September water Ni

-63 result of 11.8 +/- 10.8 Bq/L was higher than the known value of 8.55 Bq/L, exceeding the upper acceptance range of 11.12 Bq/L. The Ni-63 half-life is approximately 100 years. Nickel

-63 is considered to be a "soft" or low energy beta emitter, which means that the beta energy is very low. The maximum beta energy for Ni

-63 is approximately 65 keV, much lower than other more common nuclides such as Co

-60 (maximum beta energy of 1549 keV). The original sample was run with a 10 mL aliquot which was not sufficient for the low level of Ni

-63 in the sample. The rerun aliquot of 30 mL produced an acceptable result of 8.81 Bq/L. NCR 15

-21 6. Teledyne Brown Engineering's MAPEP September air particulate Sr-90 result of 1.48 Bq/sample was lower than the known value of 2.18 Bq/sample, exceeding the lower acceptance range of 1.53 Bq/sample. In the past, MAPEP has added substances (unusual compounds found in DOE complexes) to various matrices that have resulted in incomplete removal of the isotope of interest for the laboratories analyzing the cross checks. TBE suspects that this may be the cause of this error.

Many compounds, if not properly accounted for or removed in the sample matrix, can cause interferences to either indicate lower activity or higher activity. TBE will no longer analyze the air particulate Sr

-90 through MAPEP but will participate in the Analytics cross check program to perform both Sr-89 and Sr-90 in the air particulate matrix. NCR 15-21 7. Teledyne Brown Engineering's MAPEP September vegetation Sr

-90 result of 0.386 Bq/sample was lower than the known value of 1.30 Bq/sample, exceeding the lower acceptance range of 0.91 Bq/sample. In the past, MAPEP has added substances (unusual compounds found in DOE complexes) to various matrices that have resulted in incomplete removal of the isotope of interest for the laboratories analyzing the cross checks. TBE suspects that this maybe the cause of this error. Many compounds, if not properly accounted for or removed in the sample matrix, can cause interferences to either indicate lower activity or higher activity.

Results from previous performance evaluations were reviewed and shown to be acceptable. NCR 15-21 8. & 9.Teledyne Brown Engineering's ERA May water Sr-89/90 result s of 45.2 and 28.0 pCi/L, respectively were lower than the known value s of 63.2 and 41.9 pCi/L, respectively, exceeding the lower acceptance limit s of 51.1 and 30.8 pCi/L, respectively. The yields were on the high side of the TBE acceptance range, which indicates the present of excess calcium contributed to the yield, resulting in low results. NCR 15-0 9 10. Teledyne Brown Engineering's ERA November water Uranium natural result of 146.9 pCi/L was higher than the known value of 56.2 pCi/L, exceeding the upper acceptance limit of 62.4 pCi/L.

The technician failed to dilute the original sample, but used the entire 12 mL sample. When the results were recalculated without the dilution and using the 12 mL aliquot, the result of 57.16 agreed with the assigned value of 56.2. NCR 15

-19 The Inter-Laboratory Comparison Program provides evidence of "in control" counting systems and methods, and that the laboratories are producing accurate and reliable data.

Intentionally left blank APPENDIX A RADIOLOGICAL ENVIRONMENTAL MONITORING REPORT ANNUAL

SUMMARY

Intentionally left blank

THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUESFRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FORBRAIDWOOD STATION, 2015NAME OF FACILITY: BRAIDWOOD DOCKET NUMBER: 50-456 & 50-457 2015LOCATION OF FACILITY: BRACEVILLE, IL REPORTING PERIOD: ANNUALINDICATORCONTROLLOCATION WITH HIGHEST ANNUAL MEAN (M)LOCATIONSLOCATIONMEDIUM ORTYPES OFNUMBER OFREQUIREDMEAN (M)MEAN (M)MEAN (M)STATION #NUMBER OFPATHWAY SAMPLEDANALYSISANALYSISLOWER LIMIT(F)(F)(F)NAMENONROUTINE(UNIT OFPERFORMEDPERFORMEDOF DETECTIONRANGERANGERANGEDISTANCE AND DIRECTIONREPORTEDMEASUREMENT)(LLD)MEASUREMENTSSURFACE WATERGR-B 67 45.56.79.1BD-40 INDICATOR 0(PCI/LITER)(48/55)(11/12)(12/12)BRAIDWOOD STATION COOLING LAKE(2.3/12.7)(3.9/12.7)(6.0/12.7)ONSITEH-3 24 200 267<LLD 267BD-10 INDICATOR 0(1/20)(1/4)KANKAKEE RIVER DOWNSTREAM5.4 MILES NE OF SITENI-63 67 30<LLD<LLD- 0GAMMA 67MN-54 15<LLD<LLD- 0CO-58 15<LLD<LLD- 0FE-59 30<LLD<LLD- 0CO-60 15<LLD<LLD- 0ZN-65 30<LLD<LLD- 0

THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUESFRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FORBRAIDWOOD STATION, 2015NAME OF FACILITY: BRAIDWOOD DOCKET NUMBER: 50-456 & 50-457 2015LOCATION OF FACILITY: BRACEVILLE, IL REPORTING PERIOD: ANNUALINDICATORCONTROLLOCATION WITH HIGHEST ANNUAL MEAN (M)LOCATIONSLOCATIONMEDIUM ORTYPES OFNUMBER OFREQUIREDMEAN (M)MEAN (M)MEAN (M)STATION #NUMBER OFPATHWAY SAMPLEDANALYSISANALYSISLOWER LIMIT(F)(F)(F)NAMENONROUTINE(UNIT OFPERFORMEDPERFORMEDOF DETECTIONRANGERANGERANGEDISTANCE AND DIRECTIONREPORTEDMEASUREMENT)(LLD)MEASUREMENTSSURFACE WATERNB-95 15<LLD<LLD- 0(PCI/LITER)ZR-95 30<LLD<LLD- 0I-131 15<LLD<LLD- 0CS-134 15<LLD<LLD- 0CS-137 18<LLD<LLD- 0BA-140 60<LLD<LLD- 0LA-140 15<LLD<LLD- 0PUBLIC WATERGR-B 12 43.7 NA3.7BD-22 INDICATOR 0(PCI/LITER)(10/12)(10/12)WILMINGTON(2.3/6.4)(2.3/6.4)6.0 MILES NE OF SITE

THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUESFRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FORBRAIDWOOD STATION, 2015NAME OF FACILITY: BRAIDWOOD DOCKET NUMBER: 50-456 & 50-457 2015LOCATION OF FACILITY: BRACEVILLE, IL REPORTING PERIOD: ANNUALINDICATORCONTROLLOCATION WITH HIGHEST ANNUAL MEAN (M)LOCATIONSLOCATIONMEDIUM ORTYPES OFNUMBER OFREQUIREDMEAN (M)MEAN (M)MEAN (M)STATION #NUMBER OFPATHWAY SAMPLEDANALYSISANALYSISLOWER LIMIT(F)(F)(F)NAMENONROUTINE(UNIT OFPERFORMEDPERFORMEDOF DETECTIONRANGERANGERANGEDISTANCE AND DIRECTIONREPORTEDMEASUREMENT)(LLD)MEASUREMENTSPUBLIC WATERH-3 12 200 330 NA 330BD-22 INDICATOR 0(PCI/LITER)(9/12)(9/12)WILMINGTON(220/572)(220/572)6.0 MILES NE OF SITEI-131 12 1<LLD NA- 0GAMMA 12MN-54 15<LLD NA- 0CO-58 15<LLD NA- 0FE-59 30<LLD NA- 0CO-60 15<LLD NA- 0ZN-65 30<LLD NA- 0NB-95 15<LLD NA- 0

THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUESFRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FORBRAIDWOOD STATION, 2015NAME OF FACILITY: BRAIDWOOD DOCKET NUMBER: 50-456 & 50-457 2015LOCATION OF FACILITY: BRACEVILLE, IL REPORTING PERIOD: ANNUALINDICATORCONTROLLOCATION WITH HIGHEST ANNUAL MEAN (M)LOCATIONSLOCATIONMEDIUM ORTYPES OFNUMBER OFREQUIREDMEAN (M)MEAN (M)MEAN (M)STATION #NUMBER OFPATHWAY SAMPLEDANALYSISANALYSISLOWER LIMIT(F)(F)(F)NAMENONROUTINE(UNIT OFPERFORMEDPERFORMEDOF DETECTIONRANGERANGERANGEDISTANCE AND DIRECTIONREPORTEDMEASUREMENT)(LLD)MEASUREMENTSPUBLIC WATERZR-95 30<LLD NA- 0(PCI/LITER)CS-134 15<LLD NA- 0CS-137 18<LLD NA- 0BA-140 60<LLD NA- 0LA-140 15<LLD NA- 0GROUND WATERH-3 32 200<LLD NA- 0(PCI/LITER)GAMMA 30MN-54 15<LLD NA- 0CO-58 15<LLD NA- 0

THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUESFRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FORBRAIDWOOD STATION, 2015NAME OF FACILITY: BRAIDWOOD DOCKET NUMBER: 50-456 & 50-457 2015LOCATION OF FACILITY: BRACEVILLE, IL REPORTING PERIOD: ANNUALINDICATORCONTROLLOCATION WITH HIGHEST ANNUAL MEAN (M)LOCATIONSLOCATIONMEDIUM ORTYPES OFNUMBER OFREQUIREDMEAN (M)MEAN (M)MEAN (M)STATION #NUMBER OFPATHWAY SAMPLEDANALYSISANALYSISLOWER LIMIT(F)(F)(F)NAMENONROUTINE(UNIT OFPERFORMEDPERFORMEDOF DETECTIONRANGERANGERANGEDISTANCE AND DIRECTIONREPORTEDMEASUREMENT)(LLD)MEASUREMENTSGROUND WATERFE-59 30<LLD NA- 0(PCI/LITER)CO-60 15<LLD NA- 0ZN-65 30<LLD NA- 0NB-95 15<LLD NA- 0ZR-95 30<LLD NA- 0I-131 15<LLD NA- 0CS-134 15<LLD NA- 0CS-137 18<LLD NA- 0

THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUESFRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FORBRAIDWOOD STATION, 2015NAME OF FACILITY: BRAIDWOOD DOCKET NUMBER: 50-456 & 50-457 2015LOCATION OF FACILITY: BRACEVILLE, IL REPORTING PERIOD: ANNUALINDICATORCONTROLLOCATION WITH HIGHEST ANNUAL MEAN (M)LOCATIONSLOCATIONMEDIUM ORTYPES OFNUMBER OFREQUIREDMEAN (M)MEAN (M)MEAN (M)STATION #NUMBER OFPATHWAY SAMPLEDANALYSISANALYSISLOWER LIMIT(F)(F)(F)NAMENONROUTINE(UNIT OFPERFORMEDPERFORMEDOF DETECTIONRANGERANGERANGEDISTANCE AND DIRECTIONREPORTEDMEASUREMENT)(LLD)MEASUREMENTSGROUND WATERBA-140 60<LLD NA- 0(PCI/LITER)LA-140 15<LLD NA- 0FISHNI-63 12 260<LLD<LLD- 0(PCI/KG WET)GAMMA 12MN-54 130<LLD<LLD- 0CO-58 130<LLD<LLD- 0FE-59 260<LLD<LLD- 0CO-60 130<LLD<LLD- 0ZN-65 260<LLD<LLD- 0

THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUESFRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FORBRAIDWOOD STATION, 2015NAME OF FACILITY: BRAIDWOOD DOCKET NUMBER: 50-456 & 50-457 2015LOCATION OF FACILITY: BRACEVILLE, IL REPORTING PERIOD: ANNUALINDICATORCONTROLLOCATION WITH HIGHEST ANNUAL MEAN (M)LOCATIONSLOCATIONMEDIUM ORTYPES OFNUMBER OFREQUIREDMEAN (M)MEAN (M)MEAN (M)STATION #NUMBER OFPATHWAY SAMPLEDANALYSISANALYSISLOWER LIMIT(F)(F)(F)NAMENONROUTINE(UNIT OFPERFORMEDPERFORMEDOF DETECTIONRANGERANGERANGEDISTANCE AND DIRECTIONREPORTEDMEASUREMENT)(LLD)MEASUREMENTSFISHNB-95 NA<LLD<LLD- 0(PCI/KG WET)ZR-95 NA<LLD<LLD- 0I-131 NA<LLD<LLD- 0CS-134 130<LLD<LLD- 0CS-137 150<LLD<LLD- 0BA-140 NA<LLD<LLD- 0FISHLA-140 NA<LLD<LLD- 0(PCI/KG WET)SEDIMENTNI-63 6 260<LLD<LLD- 0(PCI/KG DRY)

THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUESFRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FORBRAIDWOOD STATION, 2015NAME OF FACILITY: BRAIDWOOD DOCKET NUMBER: 50-456 & 50-457 2015LOCATION OF FACILITY: BRACEVILLE, IL REPORTING PERIOD: ANNUALINDICATORCONTROLLOCATION WITH HIGHEST ANNUAL MEAN (M)LOCATIONSLOCATIONMEDIUM ORTYPES OFNUMBER OFREQUIREDMEAN (M)MEAN (M)MEAN (M)STATION #NUMBER OFPATHWAY SAMPLEDANALYSISANALYSISLOWER LIMIT(F)(F)(F)NAMENONROUTINE(UNIT OFPERFORMEDPERFORMEDOF DETECTIONRANGERANGERANGEDISTANCE AND DIRECTIONREPORTEDMEASUREMENT)(LLD)MEASUREMENTSSEDIMENTGAMMA 6(PCI/KG DRY)MN-54 NA<LLD<LLD- 0CO-58 NA<LLD<LLD- 0FE-59 NA<LLD<LLD- 0CO-60 NA<LLD<LLD- 0ZN-65 NA<LLD<LLD- 0NB-95 NA<LLD<LLD- 0ZR-95 NA<LLD<LLD- 0CS-134 150<LLD<LLD- 0

THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUESFRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FORBRAIDWOOD STATION, 2015NAME OF FACILITY: BRAIDWOOD DOCKET NUMBER: 50-456 & 50-457 2015LOCATION OF FACILITY: BRACEVILLE, IL REPORTING PERIOD: ANNUALINDICATORCONTROLLOCATION WITH HIGHEST ANNUAL MEAN (M)LOCATIONSLOCATIONMEDIUM ORTYPES OFNUMBER OFREQUIREDMEAN (M)MEAN (M)MEAN (M)STATION #NUMBER OFPATHWAY SAMPLEDANALYSISANALYSISLOWER LIMIT(F)(F)(F)NAMENONROUTINE(UNIT OFPERFORMEDPERFORMEDOF DETECTIONRANGERANGERANGEDISTANCE AND DIRECTIONREPORTEDMEASUREMENT)(LLD)MEASUREMENTSSEDIMENTCS-137 180 155<LLD 168BD-10 INDICATOR 0(PCI/KG DRY)(2/4)(1/2)KANKAKEE RIVER DOWNSTREAM(142/168)5.4 MILES NE OF SITEBA-140 NA<LLD<LLD- 0LA-140 NA<LLD<LLD- 0AIR PARTICULATEGR-B 412 10 17 17 18BD-04 INDICATOR 0(E-3 PCI/CU.METER)(361/362)(50/50)(52/52)ESSEX(5/43)(6/32)(5/34)4.8 MILES SSE OF SITEGAMMA 32MN-54 NA<LLD<LLD- 0CO-58 NA<LLD<LLD- 0FE-59 NA<LLD<LLD- 0CO-60 NA<LLD<LLD- 0

THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUESFRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FORBRAIDWOOD STATION, 2015NAME OF FACILITY: BRAIDWOOD DOCKET NUMBER: 50-456 & 50-457 2015LOCATION OF FACILITY: BRACEVILLE, IL REPORTING PERIOD: ANNUALINDICATORCONTROLLOCATION WITH HIGHEST ANNUAL MEAN (M)LOCATIONSLOCATIONMEDIUM ORTYPES OFNUMBER OFREQUIREDMEAN (M)MEAN (M)MEAN (M)STATION #NUMBER OFPATHWAY SAMPLEDANALYSISANALYSISLOWER LIMIT(F)(F)(F)NAMENONROUTINE(UNIT OFPERFORMEDPERFORMEDOF DETECTIONRANGERANGERANGEDISTANCE AND DIRECTIONREPORTEDMEASUREMENT)(LLD)MEASUREMENTSAIR PARTICULATEZN-65 NA<LLD<LLD- 0(E-3 PCI/CU.METER)NB-95 NA<LLD<LLD- 0ZR-95 NA<LLD<LLD- 0CS-134 50<LLD<LLD- 0CS-137 60<LLD<LLD- 0BA-140 NA<LLD<LLD- 0LA-140 NA<LLD<LLD- 0AIR IODINEGAMMA 411(E-3 PCI/CU.METER)I-131 70<LLD<LLD- 0

THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUESFRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FORBRAIDWOOD STATION, 2015NAME OF FACILITY: BRAIDWOOD DOCKET NUMBER: 50-456 & 50-457 2015LOCATION OF FACILITY: BRACEVILLE, IL REPORTING PERIOD: ANNUALINDICATORCONTROLLOCATION WITH HIGHEST ANNUAL MEAN (M)LOCATIONSLOCATIONMEDIUM ORTYPES OFNUMBER OFREQUIREDMEAN (M)MEAN (M)MEAN (M)STATION #NUMBER OFPATHWAY SAMPLEDANALYSISANALYSISLOWER LIMIT(F)(F)(F)NAMENONROUTINE(UNIT OFPERFORMEDPERFORMEDOF DETECTIONRANGERANGERANGEDISTANCE AND DIRECTIONREPORTEDMEASUREMENT)(LLD)MEASUREMENTSMILKI-131 36 1<LLD NA- 0(PCI/LITER)GAMMA 36MN-54 NA<LLD NA- 0CO-58 NA<LLD NA- 0FE-59 NA<LLD NA- 0CO-60 NA<LLD NA- 0ZN-65 NA<LLD NA- 0NB-95 NA<LLD NA- 0ZR-95 NA<LLD NA- 0

THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUESFRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FORBRAIDWOOD STATION, 2015NAME OF FACILITY: BRAIDWOOD DOCKET NUMBER: 50-456 & 50-457 2015LOCATION OF FACILITY: BRACEVILLE, IL REPORTING PERIOD: ANNUALINDICATORCONTROLLOCATION WITH HIGHEST ANNUAL MEAN (M)LOCATIONSLOCATIONMEDIUM ORTYPES OFNUMBER OFREQUIREDMEAN (M)MEAN (M)MEAN (M)STATION #NUMBER OFPATHWAY SAMPLEDANALYSISANALYSISLOWER LIMIT(F)(F)(F)NAMENONROUTINE(UNIT OFPERFORMEDPERFORMEDOF DETECTIONRANGERANGERANGEDISTANCE AND DIRECTIONREPORTEDMEASUREMENT)(LLD)MEASUREMENTSMILKCS-134 15<LLD NA- 0(PCI/LITER)CS-137 18<LLD NA- 0BA-140 60<LLD NA- 0LA-140 15<LLD NA- 0VEGETATIONGAMMA 4(PCI/KG WET)MN-54 NA<LLD<LLD- 0CO-58 NA<LLD<LLD- 0FE-59 NA<LLD<LLD- 0CO-60 NA<LLD<LLD- 0

THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUESFRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL

SUMMARY

FORBRAIDWOOD STATION, 2015NAME OF FACILITY: BRAIDWOOD DOCKET NUMBER: 50-456 & 50-457 2015LOCATION OF FACILITY: BRACEVILLE, IL REPORTING PERIOD: ANNUALINDICATORCONTROLLOCATION WITH HIGHEST ANNUAL MEAN (M)LOCATIONSLOCATIONMEDIUM ORTYPES OFNUMBER OFREQUIREDMEAN (M)MEAN (M)MEAN (M)STATION #NUMBER OFPATHWAY SAMPLEDANALYSISANALYSISLOWER LIMIT(F)(F)(F)NAMENONROUTINE(UNIT OFPERFORMEDPERFORMEDOF DETECTIONRANGERANGERANGEDISTANCE AND DIRECTIONREPORTEDMEASUREMENT)(LLD)MEASUREMENTSVEGETATIONZN-65 NA<LLD<LLD- 0(PCI/KG WET)NB-95 NA<LLD<LLD- 0ZR-95 NA<LLD<LLD- 0CS-134 60<LLD<LLD- 0CS-137 80<LLD<LLD- 0BA-140 NA<LLD<LLD- 0LA-140 NA<LLD<LLD- 0DIRECT RADIATIONOSLD-QUARTERLY 341 NA20.920.626.3BD-105-4 INDICATOR 0(MILLIREM/QTR.)(333/333)(8/8)(4/4)(13.8/31.3)(19.1/23.8)(22.8/31.3)0.20 MILES SE

Intentionally left blank APPENDIX B

LOCATION DESIGNATION, DISTANCE & DIRECTION, AND SAMPLE COLLECTION & ANALYTICAL METHODS TABLE B-1: Radiological Environmental Monitoring Program - Sampling Locations, Distance and Direction, Braidwood Station, 2015 ____________________________________________________________________________________________

Location Location Description Distance & Direction From Site ____________________________________________________________________________________________

A. Surface Water BD-10 Kankakee River Downstream (indicator)

5.4 miles

NE BD-25 Kankakee River Upstream (control)

9.6 miles

E BD-38 Main Drainage Ditch (indicator)

1.5 miles

S E BD-40 Braidwood Station Cooling Lake (indicator)

Onsite BD-55 North Pond Fatlan Site (indicator) 0.6 miles NE BD-56 South Pond Fatlan Site (indictor)

0.6 miles

NE B. Drinking (Potable) Water BD-22 Wilmington (indicator)

6.0 miles

NE C. Ground/Well Water BD-13 Braidwood City Hall Well (indicator)

1.7 miles

NNE BD-34 Gibson Well (indicator)

4.7 miles

E BD-35 Joly Well (indicator)

4.7 miles

E BD-36 Hutton Well (indicator)

4.7 miles

E BD-37 Nurczyk Well (indicator)

4.7 miles

E BD-50 Skole Well (indicator)

4.7 miles

E BD-51 Fatlan Well (indicator)

0.6 miles

NE BD-54 Cash Well (indicator)

0.9 miles

NE D. Milk - bi-weekly / monthly BD-17 Halpin's Dairy (indicator)

5.5 miles

SSW BD-18 Biros' Farm (control)

8.7 miles

W E. Air Particulates / Air Iodine BD-02 Custer Park (indicator)

5.0 miles

E BD-03 County Line Road (control)

6.2 miles

ESE BD-04 Essex (indicator)

4.8 miles

SSE BD-05 Gardner (indicator)

5.5 miles

SW BD-06 Godley (indicator)

0.5 miles

WSW BD-19 Nearsite NW (indicator)

0.3 miles

NW BD-20 Nearsite N (indicator)

0.6 miles

N BD-21 Nearsite NE (indicator)

0.5 miles

NE F. Fish BD-25 Kankakee River, Upstream (control)

9.6 miles

E BD-28 Kankakee River, Discharge (indicator)

5.4 miles

E BD-41 Cooling Lake (indicator) 1.0 mile E G. Sediment BD-10 Kankakee River, Downstream (indicator)

5.4 miles

NE BD-25 Kankakee River Upstream (control)

9.6 miles

E BD-57 Circulating Water Blowdown Discharge (indicator)

5.4 miles

E

TABLE B-1: Radiological Environmental Monitoring Program - Sampling Locations, Distance and Direction, Braidwood Station, 2015 ____________________________________________________________________________________________

Location Location Description Distance & Direction From Site ____________________________________________________________________________________________

H. Food Products Quadrant 1 Clark Farm

3.8 miles

ENE Quadrant 2 W.F. Soltwisch

4.5 miles

SSE Quadrant 3 Terri Schultz

4.8 miles

SSW Quadrant 4 Bruce Sinkular

1.9 miles

NNW Control Gorman Farm

9.0 miles

NE I. Environmental Dosimetry - OS LD Inner Ring BD-101-3 an d -4 0.5 miles N BD-102-1 and -2 1.1 miles NNE BD-103-1 and -2 1.0 mile NE BD-104-1 and -2 0.7 miles ENE BD-105-1 and -2 2.2 miles E BD-106-1 and -2 2.5 miles ESE BD-107-1 and -2 3.2 miles SE BD-108-1 and -2 3.2 miles SSE BD-109-1 and -2 3.8 miles S BD-110-1 and -2 2.8 miles SSW BD-111a-1 and -2 1.4 miles SW BD-112-1 and -2 0.7 miles WSW BD-113a-1 and -2 0.5 miles W BD-114-1 and -2 0.4 miles WNW BD-115-1 and -2 0.3 miles NW BD-116-1 0.4 miles NNW BD-116-2 0.5 miles NNW Outer Ring BD-201-1 and -2 4.2 miles N BD-202-1 and -2 4.8 miles NNE BD-203-1 and -2 4.9 miles NE BD-204-1 and -2 4.3 miles ENE BD-205-1 and -2 4.0 miles E BD-206-1 and -2 4.5 miles ESE BD-207-1 and -2 4.5 miles SE BD-208-1 an d -2 4.5 miles SSE BD-209-1 and -2 4.8 miles S BD-210-1 and -2 5.3 miles SSW BD-211-1 and -2 4.8 miles SW BD-212-3 and -4 5.0 miles WSW BD-213-3 and -4 4.8 miles W BD-214-1 and -2 4.3 miles WNW BD-215-1 and -2 4.5 miles NW BD-216-1 a nd -2 4.0 miles NNW Other BD-02-1 and -2 Custer Park (indicator)

5.0 miles

E BD-04-1 and -2 Essex (indicator)

4.8 miles

SSE BD-05-1 and -2 Gardner (indicator)

5.5 miles

SW BD-06-1 and -2 Godley (indicator)

0.5 miles

WSW BD-19-1 and -2 Nearsite NW (indicator)

0.3 miles

NW BD-20-1 and -2 Nearsite N (indicator)

0.6 miles

N BD-21-1 and -2 Nearsite NE (indicator)

0.5 miles

NE

TABLE B-1: Radiological Environmental Monitoring Program - Sampling Locations, Distance and Direction, Braidwood Station, 2015 ____________________________________________________________________________________________

Location Location Description Distance & Direction From Site ____________________________________________________________________________________________

I. Environmental Dosimetry - OSLD (cont'd) Control BD-03-1 and -2 13000 W. Road

6.2 miles

ES E ISFSI BD-104-3 and -4 0.12 miles E BD-105-3 and -4 0.22 miles S E BD-110-3 and -4 0.17 miles S E Distance in Miles from the Braidwood Station ISFSI Pad, 201 5 Sector Residence Miles (N) W 0.7 (P) WNW 0.7 (Q) NW 0.7 (R) NNW 0.7

Distance in Miles from the Braidwood Station Reactor Buildings, 201 5 Sector Residence Miles Livestock Miles Milk Farm Miles (A) N 0.5 2.6 - (B) NNE 0.9 - - (C) NE 0.7 0.9 - (D) ENE 0.8 3.3 - (E) E 1.5 2.3 - (F) ESE 2.2 2.3 - (G) SE 2.7 2.7 - (H) SSE 4.5 - - (J) S 4.2 4.8 - (K) SSW 1.3 5.3 5.5 (L) SW 0.4 1.2 - (M) WSW 0.5 - - (N) W 0.4 1.6 8.7 (P) WNW 0.4 - - (Q) NW 0.4 - - (R) NNW 0.4 - -

TABLE B-2: Radiological Environmental Monitoring Program - Summary of Sample Collection and Analytical Methods, Braidwood Station, 2015 Sample Medium Analysis Sampling Method Analytical Procedure Number Surface Water Gamma Spectroscopy Monthly composite from weekly grab samples. TBE, TBE-2007 Gamma emitting radioisotope analysis Surface Water Gross Beta Monthly composite from weekly grab samples. TBE, TBE-2008 Gross Alpha and/or Gross Beta activity in various matrices Surface Water Tritium Quarterly composite from weekly grab samples. TBE, TBE-2011 Tritium analysis in drinking water by liquid

scintillation

Surface Water Nickel-63 Monthly composite from weekly grab samples. TBE, TBE-2013 Radionickel activity in various matrices

Drinking Water Gross Beta Monthly composite from weekly composite samples. TBE, TBE-2008 Gross Alpha and/or Gross Beta activity in various matrices Drinking Water Gamma Spectroscopy Monthly composite from weekly composite samples. TBE, TBE-2007 Gamma emitting radioisotope analysis Drinking Water Tritium Monthly composite from weekly composite samples. TBE, TBE-2011 Tritium analysis in drinking water by liquid

scintillation Drinking Water Iodine Monthly composite from weekly composite samples.

TBE, TBE-2031 Radioactive Iodine in drinking water Ground/Well Water Gamma Spectroscopy Quarterly grab samples. TBE, TBE-2007 Gamma emitting radioisotope analysis

Ground/Well Water Tritium Quarterly grab samples. TBE, TBE-2011 Tritium analysis in drinking water by liquid

scintillation Fish Nickel-63 Semi-annual samples collected via electroshocking or other techniques TBE, TBE-2013 Radionickel activity in various matrices Fish Gamma Spectroscopy Samples collected twice annually via electro-shocking or other techniques TBE-2007 Gamma emitting radioisotope analysis

Sediment Gamma Spectroscopy Semi-annual grab samples TBE, TBE-2007 Gamma emitting radioisotope analysis Sediment Nickel-63 Semi-annual grab samples TBE, TBE-2013 Radionickel activity in various matrices

TABLE B-2: Radiological Environmental Monitoring Program - Summary of Sample Collection and Analytical Methods, Braidwood Station, 2015 Sample Medium Analysis Sampling Method Analytical Procedure Number Air Particulates Gross Beta One-week composite of continuous air sampling through glass fiber filter paper TBE, TBE-2008 Gross Alpha and/or gross beta activity in various matrices

Air Particulates Gamma Spectroscopy Quarterly composite of each station TBE, TBE-2007 Gamma emitting radioisotope analysis Air Iodine Gamma Spectroscopy Weekly composite of continuous air sampling through charcoal filter TBE, TBE-2007 Gamma emitting radioisotope analysis

Milk I-131 Bi-weekly grab sample May through October. Monthly all other times TBE, TBE-2012 Radioiodine in various matrices

Milk Gamma Spectroscopy Bi-weekly grab sample May through October. Monthly all other times TBE, TBE-2007 Gamma emitting radioisotope analysis

Food Products Gamma Spectroscopy Annual grab samples. TBE, TBE-2007 Gamma emitting radioisotope analysis OSLD Optically Stimulated Luminescence Dosimetry Quarterly OSLDs comprised of two

Al 2 O 3:C Landauer Incorporated element s. Landauer Incorporated Figure B-1 Inner Ring and Other OSLD Locations of the Braidwood Station, 2015

Figure B-2 Fixed Air Sampling and Outer Ring OSLD Locations of the Braidwood Station, 2015

OSLD Locations

Figure B-3 Ingestion and Waterborne Exposure Pathway Sample Locations of the Braidwood Station, 2015

Intentionally left blank APPENDIX C DATA TABLES AND FIGURES PRIMARY LABORATORY

Intentionally left blank Table C-I.1CONCENTRATIONS OF GROSS BETA IN SURFACE WATER SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMACOLLECTIONBD-10BD-25BD-38BD-40BD-55BD-56PERIOD01/08/15-01/29/156.2+/-2.212.7+/-3.45.4+/-3.0(1)10.0+/-2.9(1)(1)02/05/15-02/26/154.5+/-2.011.8+/-2.9(1)8.3+/-2.4(1)(1)03/19/15-03/26/155.3+/-2.05.8+/-2.43.9+/-2.16.0+/-2.42.6+/-1.7<2.4(1)04/01/15-04/30/153.6+/-2.56.7+/-2.97.2+/-3.311.1+/-3.42.8+/-1.8<3.605/07/15-05/28/153.3+/-2.04.5+/-2.24.0+/-2.26.4+/-2.4<2.5<3.006/04/15-06/25/154.7+/-2.06.1+/-2.3<3.17.2+/-2.43.1+/-1.8<2.907/02/15-07/30/154.0+/-1.86.9+/-2.2<3.19.0+/-2.43.5+/-1.74.8+/-2.008/06/15-08/27/155.2+/-2.14.9+/-2.15.5+/-2.611.7+/-2.63.2+/-1.75.2+/-2.209/03/15-09/24/153.4+/-1.83.9+/-1.83.3+/-2.28.7+/-2.42.3+/-1.55.1+/-2.010/01/15-10/29/153.4+/-1.9<2.73.4+/-2.27.8+/-2.42.5+/-1.65.6+/-2.111/05/15-11/25/153.9+/-1.94.7+/-2.18.8+/-3.112.7+/-3.03.3+/-1.76.7+/-2.312/03/15-12/31/153.3+/-1.75.5+/-1.94.4+/-2.110.5+/-2.53.7+/-1.64.8+/-2.0MEAN4.2+/-1.96.7+/-5.85.1+/-3.79.1+/-4.23.0+/-0.95.4+/-1.4Table C-I.2CONCENTRATIONS OF TRITIUM IN SURFACE WATER SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMACOLLECTIONBD-10BD-25BD-38BD-40BD-55BD-56PERIOD01/08/15-03/26/15 267+/-139<199<198<199<195<19604/01/15-06/25/15<188<185<191<189<183<18707/02/15-09/24/15<187<196<196<197<194<19310/01/15-12/31/15<188<190<187<189<185<187MEAN 267+/-0-----Table C-I.3CONCENTRATIONS OF NI-63 IN SURFACE WATER SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMACOLLECTIONBD-10BD-25BD-38BD-40BD-55BD-56PERIOD01/29/15-01/29/15<17<18<17(1)<16(1)(1)02/05/15-02/26/15<25<25(1)<21(1)(1)03/19/15-03/26/15<14<14<15<15<14(1)<14(1)04/01/15-04/30/15<14<16<14<14<14<1505/07/15-05/28/15<4<4<4<4<4<406/04/15-06/25/15<28<28<28<29<27<2807/02/15-07/30/15<14<14<11<14<13<1308/06/15-08/27/15<15<15<15<15<15<409/03/15-09/24/15<16<16<15<15<15<1510/01/15-10/29/15<18<18<18<18<17<1711/05/15-11/25/15<15<15<14<15<14<1412/03/15-12/31/15<14<14<14<14<14<14MEAN--THE MEAN AND TWO STANDARD DEVIATION ARE CALCULATED USING THE POSITIVE VALUES(1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION Table C-I.4CONCENTRATIONS OF GAMMA EMITTERS IN SURFACE WATER SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMASITECOLLECTIONMn-54Co-58Fe-59Co-60Zn-65Nb-95Zr-95I-131Cs-134Cs-137Ba-140La-140PERIODBD-1001/08/15-01/29/15<4<4<9<4<7<5<8<13<4<5<30<902/05/15-02/26/15<1<2<4<2<3<2<3<9<1<1<16<603/05/15-03/26/15<4<4<8<3<7<4<6<10<3<4<23<804/01/15-04/30/15<1<2<4<2<3<2<3<9<1<1<16<505/07/15-05/28/15<1<2<4<1<3<2<3<9<1<2<15<506/04/15-06/25/15<4<4<9<4<7<4<8<14<4<4<27<807/02/15-07/30/15<1<2<4<1<3<2<3<9<1<1<15<508/06/15-08/27/15<3<4<9<3<8<4<7<12<4<4<28<1009/03/15-09/24/15<8<8<12<8<16<7<13<14<7<7<38<1210/01/15-10/29/15<2<3<6<3<5<3<5<11<2<3<22<711/05/15-11/25/15<4<5<10<4<9<5<9<14<4<5<33<1012/03/15-12/31/15<4<4<8<4<7<4<6<14<3<4<30<10MEAN------------BD-2501/08/15-01/29/15<5<6<13<6<10<5<8<12<4<5<31<1102/05/15-02/26/15<2<2<5<2<3<2<4<12<2<2<19<703/12/15-03/26/15<3<4<8<4<7<4<6<11<4<4<26<804/01/15-04/30/15<2<2<6<2<4<3<5<14<2<2<23<605/07/15-05/28/15<3<3<6<2<5<3<5<12<2<3<23<806/04/15-06/25/15<4<5<9<4<8<6<8<14<4<5<32<1207/02/15-07/30/15<3<3<7<3<6<3<5<14<2<3<26<908/06/15-08/27/15<3<3<8<4<7<4<6<13<3<3<25<909/03/15-09/24/15<7<5<13<7<14<7<10<13<6<6<34<710/01/15-10/29/15<2<2<4<1<3<2<3<7<1<1<14<411/05/15-11/25/15<3<3<7<3<7<3<7<12<3<3<22<612/03/15-12/31/15<4<5<10<4<9<5<8<13<4<4<27<11MEAN------------

Table C-I.4CONCENTRATIONS OF GAMMA EMITTERS IN SURFACE WATER SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMASITECOLLECTIONMn-54Co-58Fe-59Co-60Zn-65Nb-95Zr-95I-131Cs-134Cs-137Ba-140La-140PERIODBD-3801/29/15-01/29/15<4<5<10<5<8<5<9<14<5<5<30<902/05/15-02/26/15(1)03/12/15-03/26/15<4<4<8<4<7<4<6<11<4<4<25<804/01/15-04/30/15<2<2<5<2<3<2<3<11<2<2<18<605/07/15-05/28/15<2<2<4<2<3<2<3<9<1<2<16<506/04/15-06/25/15<5<5<11<5<10<5<10<13<4<6<27<907/02/15-07/30/15<2<2<3<1<3<2<3<10<1<2<17<508/06/15-08/27/15<1<1<3<1<3<2<3<7<1<1<12<409/03/15-09/24/15<6<6<13<6<15<7<13<12<6<7<30<910/01/15-10/29/15<3<3<7<2<6<3<5<11<2<3<23<811/05/15-11/25/15<4<4<8<3<8<4<7<13<4<4<29<812/03/15-12/31/15<4<5<10<4<8<5<9<15<4<5<32<9MEAN------------BD-4001/08/15-01/29/15<5<6<13<8<10<6<9<14<4<6<39<1502/05/15-02/26/15<1<2<3<1<3<2<3<10<1<1<16<403/05/15-03/26/15<4<5<9<4<8<4<8<11<4<5<26<704/01/15-04/30/15<1<1<3<1<2<1<3<7<1<1<13<305/07/15-05/28/15<2<2<4<2<4<2<4<11<2<2<20<606/04/15-06/25/15<4<4<10<6<7<4<7<15<4<4<28<1007/02/15-07/30/15<1<2<4<1<3<2<3<10<1<2<17<508/06/15-08/27/15<3<4<9<3<8<4<7<12<3<4<26<809/03/15-09/24/15<5<5<12<5<11<6<7<12<5<6<31<810/01/15-10/29/15<2<2<4<2<3<2<4<9<2<2<17<511/05/15-11/25/15<4<5<10<5<7<5<8<12<4<5<31<1412/03/15-12/31/15<3<5<9<5<8<5<9<14<4<5<28<8MEAN------------(1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION Table C-I.4CONCENTRATIONS OF GAMMA EMITTERS IN SURFACE WATER SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMASITECOLLECTIONMn-54Co-58Fe-59Co-60Zn-65Nb-95Zr-95I-131Cs-134Cs-137Ba-140La-140PERIODBD-5501/08/15-01/29/15(1)02/05/15-02/26/15(1)03/19/15-03/26/15<6<6<12<6<11<6<11<15<5<6<34<1004/01/15-04/30/15<2<3<5<2<5<3<5<15<2<2<24<705/07/15-05/28/15<2<2<5<2<3<2<3<10<2<2<19<606/04/15-06/25/15<4<4<9<6<8<4<7<15<4<4<29<907/02/15-07/30/15<2<2<6<2<4<2<4<12<2<2<20<708/06/15-08/27/15<3<3<7<4<6<4<7<11<3<3<23<709/03/15-09/24/15<7<7<17<6<11<6<12<11<6<7<36<1110/01/15-10/29/15<2<3<5<2<5<3<5<11<2<2<20<611/05/15-11/25/15<4<5<10<4<9<5<8<14<4<4<34<912/03/15-12/31/15<4<4<10<4<8<4<7<12<4<4<27<9MEAN------------BD-5601/08/15-01/29/15(1)------------02/05/15-02/26/15(1)------------03/19/15-03/26/15<5<6<13<6<9<6<9<14<5<6<32<1104/01/15-04/30/15<2<2<5<2<4<2<4<11<2<2<20<805/07/15-05/28/15<2<2<5<2<4<2<3<10<2<2<16<606/04/15-06/25/15<5<5<12<4<10<5<9<15<4<5<34<1107/02/15-07/30/15<2<2<4<2<4<2<3<10<2<2<18<708/06/15-08/27/15<4<4<9<4<8<4<7<13<3<4<28<909/03/15-09/24/15<5<6<11<5<11<5<9<10<6<5<29<810/01/15-10/29/15<2<2<5<2<4<2<4<10<2<2<19<611/05/15-11/25/15<4<4<10<4<9<4<6<13<3<4<30<1012/03/15-12/31/15<4<4<9<4<8<5<7<12<3<4<27<10MEAN------------(1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION Table C-II.1CONCENTRATIONS OF GROSS BETA IN PUBLIC WATER SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMACOLLECTIONBD-22PERIOD12/31/14-01/29/152.3+/-1.501/29/15-02/26/154.0+/-1.602/26/15-04/01/156.4+/-1.804/01/15-04/30/152.5+/-1.404/30/15-05/28/15<2.005/28/15-07/02/153.8+/-1.607/02/15-07/30/15<2.207/30/15-08/27/153.8+/-1.508/27/15-10/01/153.0+/-1.510/01/15-10/29/153.3+/-1.610/29/15-12/03/153.9+/-1.712/03/15-12/31/153.7+/-1.4MEAN3.7+/-2.3Table C-II.2CONCENTRATIONS OF TRITIUM IN PUBLIC WATER SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMACOLLECTIONBD-22PERIOD12/31/14-01/29/15 280+/-11201/29/15-02/26/15 364+/-13702/26/15-04/01/15 329+/-14004/01/15-04/30/15<19604/30/15-05/28/15<17305/28/15-07/02/15 272+/-12807/02/15-07/30/15 278+/-13507/30/15-08/27/15 257+/-12408/27/15-10/01/15<19510/01/15-10/29/15 220+/-12510/29/15-12/03/15 572+/-15212/03/15-12/31/15 395+/-134MEAN 330+/-212Table C-II.3CONCENTRATIONS OF I-131 IN PUBLIC WATER SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMACOLLECTIONBD-22PERIOD12/31/14-01/29/15<0.801/29/15-02/26/15<0.802/26/15-04/01/15<0.704/01/15-04/30/15<0.604/30/15-05/28/15<0.805/28/15-07/02/15<0.707/02/15-07/30/15<0.807/30/15-08/27/15<0.608/27/15-10/01/15<0.910/01/15-10/29/15<0.810/29/15-12/03/15<0.312/03/15-12/31/15<0.3MEAN-THE MEAN AND TWO STANDARD DEVIATION ARE CALCULATED USING THE POSITIVE VALUES Table C-II.4CONCENTRATIONS OF GAMMA EMITTERS IN PUBLIC WATER SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMASITECOLLECTIONMn-54Co-58Fe-59Co-60Zn-65Nb-95Zr-95Cs-134Cs-137Ba-140La-140PERIODBD-2212/31/14-01/29/15<2<2<4<1<3<2<3<1<1<19<701/29/15-02/26/15<1<1<3<1<2<1<2<1<1<16<402/26/15-04/01/15<1<1<3<1<2<1<2<1<1<17<604/01/15-04/30/15<1<1<2<1<2<1<1<1<1<16<404/30/15-05/28/15<1<1<2<1<2<1<2<1<1<18<505/28/15-07/02/15<2<2<5<2<4<2<4<2<2<21<607/02/15-07/30/15<2<2<5<2<4<2<4<2<2<21<707/30/15-08/27/15<2<2<4<1<3<2<3<2<2<18<508/27/15-10/01/15<2<2<5<2<5<2<4<2<2<24<710/01/15-10/29/15<2<3<6<2<5<3<5<3<3<23<610/29/15-12/03/15<7<7<15<4<12<8<12<6<6<38<1212/03/15-12/31/15<5<4<9<4<10<5<8<5<4<31<8MEAN-----------

Table C-III.1CONCENTRATIONS OF TRITIUM IN GROUND/WELL WATER SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMACOLLECTIONBD-13BD-34BD-35BD-36BD-37BD-50BD-51BD-54PERIOD01/15/15-01/15/15<159<190<191<191<195<190<154<19504/09/15-04/09/15<200<200<200<199<200<198<197<20007/10/15-07/10/15<184<188<193<179<193<193<193<19010/06/15-10/06/15<184<199<200<196<200<199<195<200MEAN--------

Table C-III.2CONCENTRATIONS OF GAMMA EMITTERS IN GROUND/WELL WATER SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMASITECOLLECTIONMn-54Co-58Fe-59Co-60Zn-65Nb-95Zr-95I-131Cs-134Cs-137Ba-140La-140PERIODBD-1301/08/15-01/08/15<5<7<10<7<16<6<9<12<6<6<34<1004/09/15-04/09/15<4<5<11<4<9<6<8<14<4<5<28<807/10/15-07/10/15<5<5<12<7<13<7<9<10<5<6<29<910/06/15-10/06/15<5<5<11<6<12<6<11<12<5<6<34<9MEAN------------BD-3401/15/15-01/15/15<5<5<9<5<10<5<8<8<4<5<24<804/09/15-04/09/15<4<4<8<3<8<4<6<12<4<4<24<807/10/15-07/10/15<7<7<16<7<16<7<11<12<6<7<34<1210/06/15-10/06/15<5<5<8<4<9<6<9<15<6<5<33<8MEAN------------BD-3501/15/15-01/15/15<6<6<11<7<13<7<11<14<6<9<36<1304/09/15-04/09/15<3<5<5<4<6<5<7<12<4<4<28<1307/10/15-07/10/15<5<4<10<6<10<5<9<8<5<5<21<810/06/15-10/06/15<6<6<12<5<12<6<11<12<5<6<33<11MEAN------------BD-3601/15/15-01/15/15<7<8<16<5<15<8<13<14<7<8<36<1104/09/15-04/09/15<3<4<8<3<6<4<6<10<3<3<22<607/10/15-07/10/15<4<4<10<5<9<5<8<8<5<5<24<610/06/15-10/06/15<4<7<12<7<9<7<11<14<7<6<35<11MEAN------------BD-3701/15/15-01/15/15<6<5<12<5<10<6<9<10<5<5<28<804/09/15-04/09/15<5<4<10<5<9<5<9<13<4<4<28<1007/10/15-07/10/15<5<5<8<6<10<5<8<8<5<5<23<810/06/15-10/06/15<5<5<11<5<10<6<10<12<5<5<28<9MEAN------------

Table C-III.2CONCENTRATIONS OF GAMMA EMITTERS IN GROUND/WELL WATER SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMASITECOLLECTIONMn-54Co-58Fe-59Co-60Zn-65Nb-95Zr-95I-131Cs-134Cs-137Ba-140La-140PERIODBD-5001/15/15-01/15/15<5<6<11<6<14<7<10<11<6<7<31<1004/09/15-04/09/15<5<5<11<6<11<5<9<14<5<5<32<1007/10/15-07/10/15<6<7<11<6<8<6<9<10<6<8<32<910/06/15-10/06/15<4<6<14<4<10<5<7<11<4<4<30<12MEAN------------BD-5101/08/15-01/08/15<4<5<8<5<9<5<8<8<4<5<24<804/09/15-04/09/15<4<5<11<5<9<5<9<14<5<4<29<807/10/15-07/10/15<8<9<19<9<18<8<14<11<7<9<37<1510/06/15-10/06/15<6<7<14<7<15<8<13<15<7<7<38<10MEAN------------BD-5401/15/15-01/15/15<7<5<14<5<12<7<8<10<5<8<26<1104/09/15-04/09/15<5<6<13<5<11<7<12<14<5<6<36<1307/10/15-07/10/15<5<7<13<6<12<7<12<10<6<7<29<810/06/15-10/06/15<6<6<9<7<11<6<9<13<6<6<29<11MEAN------------

Table C-IV.1CONCENTRATIONS OF NICKEL-63 AND GAMMA EMITTERS IN FISH SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/KG WET +/- 2 SIGMASITECOLLECTIONNi-63Mn-54Co-58Fe-59Co-60Zn-65Nb-95Zr-95I-131Cs-134Cs-137Ba-140La-140PERIODBD-25Golden Redhorse05/04/15<39<59<56<132<58<107<67<121<695<51<54<1050<377Freshwater Drum05/04/15<39<79<97<219<68<137<105<173<930<66<76<1259<249Golden Redhorse10/22/15<38<41<58<115<60<109<53<96<281<53<43<520<96Smallmouth Bass10/22/15<33<65<84<194<127<165<86<124<254<87<79<539<69MEAN-------------BD-28 Golden Redhorse05/04/15<37<56<70<160<68<118<87<148<747<68<57<1105<306Common Carp05/04/15<38<70<85<212<63<157<90<171<1032<81<78<1291<404Golden Redhorse10/22/15<41<66<85<153<28<140<56<116<218<64<62<499<73Smallmouth Bass10/22/15<43<65<84<222<66<235<119<195<290<85<98<592<157MEAN-------------BD-41 Largemouth Bass05/04/15<40<63<76<167<57<128<67<136<742<56<67<1041<275Common Carp05/04/15<32<51<70<138<47<136<69<110<694<51<52<965<247Largemouth Bass10/22/15<34<56<47<157<55<119<78<130<188<55<53<441<106Common Carp10/22/15<35<55<73<167<72<162<67<150<247<81<90<426<111MEAN-------------

Table C-V.1CONCENTRATIONS OF NICKEL-63 AND GAMMA EMITTERS IN SEDIMENT SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/KG DRY +/- 2 SIGMASITECOLLECTIONNi-63Mn-54Co-58Fe-59Co-60Zn-65Nb-95Zr-95Cs-134Cs-137Ba-140La-140PERIODBD-1005/14/15<255<68<79<189<99<202<100<156<70 168+/-88<571<13210/06/15<239<127<103<283<90<206<127<211<109<146<626<136MEAN------------BD-2505/14/15<253<83<89<220<72<203<115<190<88<141<583<17910/06/15<227<78<68<213<97<232<98<167<95<100<473<107MEAN------------BD-5705/14/15<238<106<97<254<101<275<123<195<92 142+/-85<740<25810/06/15<225<74<69<107<82<194<86<142<48<104<442<82MEAN------------

Table C-VI.1CONCENTRATIONS OF GROSS BETA IN AIR PARTICULATE SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF E-3 PCI/CU METER +/- 2 SIGMACOLLECTIONGROUP II - FAR FIELDPERIODBD-06BD-19BD-20BD-21BD-02BD-04BD-05BD-0312/31/14-01/08/15 31+/-5 25+/-4 21+/-4 26+/-5 28+/-5 22+/-4 30+/-5 18+/-401/08/15-01/15/15 21+/-5 22+/-5 17+/-4 18+/-4 21+/-5 21+/-5 22+/-5 22+/-501/15/15-01/22/15 23+/-5 28+/-5 21+/-5 26+/-5 18+/-4 23+/-5 22+/-5 20+/-501/22/15-01/29/15 14+/-4 9+/-4 12+/-4 14+/-4 13+/-4 13+/-4 12+/-4 16+/-401/29/15-02/05/15 13+/-4 12+/-4 13+/-4 19+/-3 13+/-4 17+/-4 15+/-4 16+/-402/05/15-02/12/15 23+/-4 21+/-4 20+/-4(1)21+/-4 22+/-4 22+/-4 24+/-402/12/15-02/19/15 23+/-5 21+/-5 23+/-5 22+/-5 19+/-5 17+/-5 20+/-5 25+/-502/19/15-02/26/15 32+/-5 35+/-5 30+/-5 37+/-5 36+/-5 29+/-5 31+/-5 28+/-502/26/15-03/05/15 17+/-4 15+/-4 14+/-4 17+/-4 12+/-4 17+/-4 18+/-4 21+/-503/05/15-03/12/15 15+/-4 14+/-4 13+/-4 14+/-4 15+/-4 14+/-4 15+/-4 15+/-403/12/15-03/19/15 13+/-4 16+/-4 17+/-4 12+/-4 15+/-4 12+/-4 13+/-4 14+/-403/19/15-03/26/15 14+/-4 18+/-4 14+/-4 22+/-5 17+/-4 18+/-4 18+/-4 17+/-403/26/15-04/01/15 17+/-5 17+/-5 14+/-4 13+/-4 18+/-5 13+/-4 16+/-4 14+/-404/01/15-04/09/15 11+/-3 8+/-3 14+/-4 13+/-3 14+/-3 13+/-3 9+/-3 12+/-304/09/15-04/16/15 16+/-4 15+/-4 18+/-4 14+/-4 14+/-4 17+/-4 17+/-4 17+/-404/16/15-04/23/15 12+/-4 9+/-4 15+/-4 13+/-4 13+/-4 17+/-4 12+/-4 11+/-404/23/15-04/30/15 14+/-4 9+/-3 12+/-4 11+/-4 12+/-4 12+/-4 10+/-3 14+/-404/30/15-05/07/15 9+/-4 15+/-4 15+/-4 10+/-4 12+/-4 13+/-4 13+/-4 11+/-405/07/15-05/14/15 6+/-3 5+/-3 5+/-3 5+/-3 5+/-3 5+/-3 6+/-3 6+/-305/14/15-05/21/15 11+/-4 9+/-3 13+/-4 14+/-4 10+/-3 14+/-4 9+/-3 10+/-405/21/15-05/28/15 17+/-5 14+/-4 13+/-4 12+/-4 14+/-4 12+/-4 12+/-4 13+/-405/28/15-06/04/15 9+/-4 13+/-4 13+/-4 11+/-4 11+/-4 12+/-4 11+/-4 10+/-406/04/15-06/11/15 14+/-4 16+/-4 14+/-4 14+/-4 18+/-4 15+/-4 15+/-4 13+/-406/11/15-06/18/15 6+/-3 10+/-4 9+/-4<3 9+/-4 11+/-4 9+/-4 11+/-406/18/15-06/25/15 16+/-4 12+/-4 12+/-5 12+/-5 15+/-4 12+/-4 11+/-4 15+/-506/25/15-07/02/15 9+/-4 10+/-4 10+/-4 10+/-4 10+/-4 8+/-4 10+/-4 12+/-407/02/15-07/09/15 10+/-4 8+/-4 11+/-4 12+/-4 14+/-4 11+/-4 12+/-4 7+/-307/09/15-07/16/15 8+/-4 11+/-4 13+/-4 11+/-4 9+/-4 12+/-4 9+/-4 8+/-407/16/15-07/23/15 15+/-4 14+/-4 15+/-4 16+/-4 14+/-4 18+/-4 16+/-4 12+/-407/23/15-07/30/15 14+/-5 17+/-5 21+/-5 14+/-5 17+/-5 15+/-5 13+/-4(1)07/30/15-08/06/15 21+/-5 14+/-4 21+/-5 23+/-5 21+/-5 23+/-5 22+/-5(1)08/06/15-08/13/15 19+/-4 18+/-4 16+/-4 20+/-4 20+/-4 21+/-4 21+/-4 18+/-408/13/15-08/20/15 20+/-5 17+/-5 16+/-4 19+/-5 21+/-5 18+/-5 19+/-5 15+/-408/20/15-08/27/15 14+/-4 18+/-4 17+/-4 18+/-4 17+/-4 20+/-4 19+/-4 17+/-408/27/15-09/03/15 38+/-6 36+/-5 36+/-5 36+/-5 33+/-5 34+/-5 43+/-6 32+/-509/03/15-09/10/15 33+/-5 30+/-5 30+/-5 30+/-5 32+/-5 24+/-5 30+/-5 31+/-609/10/15-09/17/15 17+/-4 18+/-4 17+/-4 20+/-4 16+/-4 24+/-4 18+/-4 20+/-409/17/15-09/24/15 20+/-4 16+/-4 17+/-4 16+/-4 14+/-4 15+/-4 15+/-4 20+/-409/24/15-10/01/15 20+/-4 22+/-5 21+/-4 19+/-4 16+/-4 19+/-4 21+/-5 20+/-410/01/15-10/08/15 15+/-4 13+/-4 12+/-4 12+/-4 12+/-4 15+/-4 15+/-4 9+/-310/08/15-10/15/15 20+/-5 25+/-5 21+/-5 19+/-4 20+/-5 19+/-5 23+/-5 18+/-410/15/15-10/22/15 29+/-5 23+/-5 25+/-5 27+/-5 23+/-5 27+/-5 27+/-5 26+/-510/22/15-10/29/15 14+/-4 14+/-4 13+/-4 11+/-4 16+/-4 18+/-4 14+/-4 12+/-410/29/15-11/05/15 19+/-4 16+/-4 18+/-4 14+/-4 17+/-4 19+/-4 20+/-4 19+/-411/05/15-11/12/15 21+/-5 17+/-4 21+/-5 24+/-5 18+/-5 24+/-5 20+/-5 20+/-511/12/15-11/19/15 17+/-4(1)19+/-4 19+/-4 18+/-4 25+/-5 19+/-4 18+/-411/19/15-11/25/15 15+/-5 19+/-13 14+/-5 13+/-5 13+/-5 14+/-5 15+/-5 18+/-511/25/15-12/03/15 19+/-4 16+/-4 20+/-4 14+/-3 17+/-4 15+/-3 18+/-4 14+/-312/03/15-12/10/15 29+/-5 25+/-5 26+/-5 30+/-5 33+/-6 34+/-6 26+/-5 27+/-512/10/15-12/17/15 13+/-4 16+/-4 15+/-4 18+/-4 14+/-4 13+/-4 15+/-4 15+/-412/17/15-12/24/15 26+/-5 21+/-4 30+/-5 22+/-5 24+/-5 28+/-5 26+/-5 21+/-412/24/15-12/31/15 16+/-4 15+/-4 14+/-4 14+/-4 14+/-4 20+/-4 15+/-4 14+/-4MEAN 17+/-14 17+/-13 17+/-12 17+/-13 17+/-13 18+/-12 17+/-14 17+/-12THE MEAN AND TWO STANDARD DEVIATION ARE CALCULATED USING THE POSITIVE VALUES(1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATIONGROUP III - CONTROL LOCATIONGROUP I - NEAR FIELD Table C-VI.2MONTHLY AND YEARLY VALUES OF GROSS BETA CONCENTRATIONS IN AIRPARTICULATE SAMPLES COLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF E-3 PCI/CU METER +/- 2 SIGMAGROUP I - NEAR FIELD LOCATIONSGROUP II - FAR FIELD LOCATIONSGROUP III - CONTROL LOCATIONSCOLLECTIONMINMAXMEAN +/-COLLECTIONMINMAXMEAN +/-COLLECTIONMINMAXMEAN +/-PERIOD2SDPERIOD2SDPERIOD2SD12/31/14-01/29/15 9 31 20+/-1212/31/14-01/29/15 12 30 20+/-1212/31/14-01/29/15 16 22 19+/-601/29/15-02/26/15 12 37 23+/-1501/29/15-02/26/15 13 36 22+/-1301/29/15-02/26/15 16 28 23+/-1002/26/15-04/01/15 12 22 15+/-502/26/15-04/01/15 12 18 15+/-402/26/15-04/01/15 14 21 16+/-604/01/15-04/30/15 8 18 13+/-504/01/15-04/30/15 9 17 13+/-504/01/15-04/30/15 11 17 13+/-604/30/15-05/28/15 5 17 11+/-804/30/15-05/28/15 5 14 10+/-704/30/15-05/28/15 6 13 10+/-505/28/15-07/02/15 6 16 12+/-505/28/15-07/02/15 8 18 12+/-605/28/15-07/02/15 10 15 12+/-407/02/15-07/30/15 8 21 13+/-707/02/15-07/30/15 9 18 13+/-607/02/15-07/23/15 7 12 9+/-607/30/15-09/03/15 14 38 22+/-1607/30/15-09/03/15 17 43 23+/-1508/06/15-09/03/15 15 32 20+/-1509/03/15-10/01/15 16 33 22+/-1109/03/15-10/01/15 14 32 20+/-1209/03/15-10/01/15 20 31 23+/-1110/01/15-10/29/15 11 29 18+/-1210/01/15-10/29/15 12 27 19+/-1010/01/15-10/29/15 9 26 16+/-1410/29/15-12/03/15 13 24 18+/-610/29/15-12/03/15 13 25 18+/-610/29/15-12/03/15 14 20 18+/-512/03/15-12/31/15 13 30 21+/-1312/03/15-12/31/15 13 34 22+/-1512/03/15-12/31/15 14 27 19+/-1212/31/14-12/31/15 5 38 17+/-1312/31/14-12/31/15 5 43 17+/-1312/31/14-12/31/15 6 32 17+/-12THE MEAN AND TWO STANDARD DEVIATION ARE CALCULATED USING THE POSITIVE VALUES Table C-VI.3CONCENTRATIONS OF GAMMA EMITTERS IN AIR PARTICULATE SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF E-3 PCI/CU METER +/- 2 SIGMASITECOLLECTIONMn-54Co-58Fe-59Co-60Zn-65Nb-95Zr-95Cs-134Cs-137Ba-140La-140PERIODBD-0212/31/14-04/01/15<4<4<12<3<11<5<11<4<3<147<6304/01/15-07/02/15<2<2<6<2<5<3<4<2<3<34<1607/02/15-10/01/15<2<3<7<2<5<3<3<2<2<53<1910/01/15-12/31/15<2<2<4<3<3<3<5<3<2<27<8MEAN-----------BD-0312/31/14-04/01/15<4<6<21<5<13<8<12<5<5<217<8404/01/15-07/02/15<3<6<7<5<7<4<7<4<3<54<1807/02/15-10/01/15<2<4<10<3<8<3<4<3<3<72<2410/01/15-12/31/15<2<2<5<2<5<2<4<2<2<23<11MEAN-----------BD-0412/31/14-04/01/15<4<4<10<3<7<6<4<4<3<131<8804/01/15-07/02/15<4<3<10<2<5<3<4<3<3<44<907/02/15-10/01/15<2<3<10<2<5<4<5<2<3<54<1710/01/15-12/31/15<3<3<6<3<6<3<6<3<3<36<6MEAN-----------BD-0512/31/14-04/01/15<3<5<16<4<8<4<6<4<3<181<6804/01/15-07/02/15<2<4<5<3<6<2<7<2<2<48<1207/02/15-10/01/15<2<3<8<2<5<3<5<3<2<53<1710/01/15-12/31/15<3<3<8<2<7<3<6<3<2<33<13MEAN-----------BD-0612/31/14-04/01/15<3<4<10<2<8<3<5<3<2<106<1704/01/15-07/02/15<3<3<7<3<7<5<6<2<2<43<2107/02/15-10/01/15<4<6<12<4<11<5<8<4<3<99<3410/01/15-12/31/15<4<4<10<5<13<4<8<4<4<40<19MEAN-----------

Table C-VI.3CONCENTRATIONS OF GAMMA EMITTERS IN AIR PARTICULATE SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF E-3 PCI/CU METER +/- 2 SIGMASITECOLLECTIONMn-54Co-58Fe-59Co-60Zn-65Nb-95Zr-95Cs-134Cs-137Ba-140La-140PERIODBD-1912/31/14-04/01/15<4<10<19<6<9<6<12<5<4<197<9704/01/15-07/02/15<3<3<6<3<6<4<6<3<2<36<1207/02/15-10/01/15<3<4<8<3<6<3<7<3<4<82<3510/01/15-12/31/15<3<3<9<4<7<4<7<3<3<46<14MEAN-----------BD-2012/31/14-04/01/15<3<4<12<4<8<4<8<3<3<165<6304/01/15-07/02/15<3<4<5<2<6<3<5<3<3<37<1207/02/15-10/01/15<3<6<10<4<9<5<10<4<3<85<3310/01/15-12/31/15<2<3<7<3<7<3<5<3<2<34<11MEAN-----------BD-2112/31/14-04/01/15<5<5<20<4<11<9<17<5<4<354<11204/01/15-07/02/15<3<3<5<2<6<3<6<2<3<46<907/02/15-10/01/15<2<3<5<1<5<3<5<3<2<48<1910/01/15-12/31/15<3<4<8<3<7<4<6<3<3<49<14MEAN-----------

Table C-VII.1CONCENTRATIONS OF I-131 IN AIR IODINE SAMPLES COLLECTED INTHE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF E-3 PCI/CU METER +/- 2 SIGMACOLLECTIONGROUP II - FAR FIELDPERIODBD-06BD-19BD-20BD-21BD-02BD-04BD-05BD-0312/31/14-01/08/15<32<32<32<32<32<32<32<3201/08/15-01/15/15<20<58<58<58<52<52<52<5201/15/15-01/22/15<63<63<63<63<58<58<58<5801/22/15-01/29/15<42<23<42<42<53<53<42<5301/29/15-02/05/15<51<51<22<7<56<56<51<5602/05/15-02/12/15<37<37<37(1)<40<40<37<4002/12/15-02/19/15<43<42<42<42<50<50<50<5002/19/15-02/26/15<45<42<42<42<17<45<45<4502/26/15-03/05/15<41<41<41<41<38<37<37<3703/05/15-03/12/15<36<37<37<37<36<36<36<1403/12/15-03/19/15<66<66<68<66<69<69<69<7003/19/15-03/26/15<38<37<37<37<37<21<37<3703/26/15-04/01/15<47<58<56<56<20<47<46<4804/01/15-04/09/15<32<33<33<33<32<32<12<3204/09/15-04/16/15<53<53<53<53<69<69<69<6904/16/15-04/23/15<26<62<62<62<62<62<62<6204/23/15-04/30/15<59<59<59<59<63<67<65<6304/30/15-05/07/15<32<17<32<31<32<32<32<3205/07/15-05/14/15<26<26<26<26<23<23<23<2305/14/15-05/21/15<46<46<19<46<49<49<49<4905/21/15-05/28/15<27<27<27<27<22<22<22<2205/28/15-06/04/15<67<67<67<28<40<40<40<4006/04/15-06/11/15<45<45<45<45<35<36<35<3506/11/15-06/18/15<37<37<37<37<59<60<60<6006/18/15-06/25/15<53<54<65<67<54<54<50(1)06/25/15-07/02/15<49<49<49<49<52<52<52<5207/02/15-07/09/15<41<41<17<41<44<44<44<4407/09/15-07/16/15<56<28<56<56<15<15<15<1507/16/15-07/23/15<41<40<41<41<46<46<46<5207/23/15-07/30/15<40<38<40<40<39<39<39<07/30/15-08/06/15<62<67<62<34<68<69<62(1)08/06/15-08/13/15<56<55<57<57<50<58<48<2208/13/15-08/20/15<19<45<45<45<29<29<28<2808/20/15-08/27/15<56<56<56<56<58<64<62<6008/27/15-09/03/15<52<52<52<52<54<56<56<5209/03/15-09/10/15<45<65<65<65<19<46<45<4909/10/15-09/17/15<45<45<45<45<57<57<55<5409/17/15-09/24/15<54<54<54<54<54<54<53<5309/24/15-10/01/15<53<54<54<22<58<58<60<5810/01/15-10/08/15<45<45<45<45<49<49<50<1810/08/15-10/15/15<60<60<60<60<35<36<36<3410/15/15-10/22/15<58<58<59<59<64<66<64<2610/22/15-10/29/15<53<53<53<53<42<43<41<4010/29/15-11/05/15<34<46<46<46<34<37<35<1211/05/15-11/12/15<43<42<43<42<42<43<44<4111/12/15-11/19/15<56(1)<58<58<69<69<69<6511/19/15-11/25/15<38(1)<38<38<40<40<39<3711/25/15-12/03/15<57<57<58<58<44<43<43<4112/03/15-12/10/15<68<68<68<69<39<39<39<3612/10/15-12/17/15<55<55<67<53<57<57<58<5412/17/15-12/24/15<66<67<67<67<68<68<68<6412/24/15-12/31/15<66<68<69<69<66<66<64<62MEAN--------(1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATIONGROUP I - NEAR FIELDGROUP III - CONTROL LOCATION 254 Table C-VIII.1CONCENTRATIONS OF I-131 IN MILK SAMPLES COLLECTED INTHE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMA INDICATOR FARMCONTROL FARMCOLLECTIONBD-17BD-18PERIOD01/15/15<0.3(1)02/06/15<0.7<0.503/05/15<0.5<0.704/02/15<0.5<0.405/07/15<0.6<0.605/21/15<0.6<0.706/04/15<0.9<0.906/18/15<0.8<0.707/02/15<0.7<0.807/16/15<0.3<0.307/30/15<0.5<0.608/13/15<0.6<0.808/27/15<0.7<0.609/10/15<0.6<0.609/24/15<0.3<0.410/08/15<0.7<0.710/22/15<0.5<0.311/05/15<0.6<0.512/03/15<0.5(1)MEAN--(1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION Table C-VIII.2CONCENTRATIONS OF GAMMA EMITTERS IN MILK SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMASITECOLLECTIONMn-54Co-58Fe-59Co-60Zn-65Nb-95Zr-95Cs-134Cs-137Ba-140La-140PERIODBD-1701/15/15<8<8<20<8<19<8<15<8<8<39<1002/06/15<7<7<17<7<17<7<13<6<7<33<903/05/15<3<4<9<4<6<4<6<3<3<22<804/02/15<5<5<12<5<12<5<8<4<5<35<905/07/15<2<2<6<2<5<2<4<2<2<17<505/21/15<3<4<9<4<8<4<6<3<4<28<906/04/15<13<12<24<15<31<12<20<11<11<54<1206/18/15<5<6<11<7<11<6<10<6<5<23<707/02/15<7<8<16<7<14<8<9<5<6<36<1507/16/15<6<6<15<7<18<6<11<5<6<39<707/30/15<5<5<14<7<14<6<9<5<6<35<808/13/15<8<9<18<9<18<9<15<9<8<50<1108/27/15<11<11<24<12<31<12<22<10<13<52<909/10/15<11<13<28<9<37<13<20<15<14<58<709/24/15<8<8<20<9<19<8<16<6<9<33<1110/08/15<6<7<14<6<14<7<11<6<7<32<810/22/15<6<6<15<6<12<5<11<6<5<25<711/05/15<8<7<23<11<24<9<16<10<11<39<1112/03/15<8<7<22<10<13<9<13<6<8<36<11MEAN-----------

Table C-VIII.2CONCENTRATIONS OF GAMMA EMITTERS IN MILK SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMASITECOLLECTIONMn-54Co-58Fe-59Co-60Zn-65Nb-95Zr-95Cs-134Cs-137Ba-140La-140PERIODBD-1801/08/15(1)02/06/15<7<6<16<6<16<7<11<7<7<33<1003/05/15<6<5<17<5<14<7<11<6<6<46<1004/02/15<8<9<18<7<17<10<16<8<9<59<905/06/15<3<3<8<3<7<3<6<3<3<28<905/21/15<8<8<14<9<18<10<16<7<8<52<1206/04/15<9<7<24<11<22<10<14<7<8<42<1406/18/15<6<9<15<5<16<7<11<6<8<37<1307/01/15<6<6<15<8<12<6<10<6<6<36<1007/16/15<9<7<15<8<14<8<14<7<7<49<1107/30/15<6<6<15<6<14<6<13<6<6<38<1508/13/15<9<9<18<8<20<9<14<9<9<48<1308/27/15<8<7<15<12<26<10<17<6<9<39<1109/10/15<6<6<15<8<15<6<12<5<7<25<909/24/15<8<6<20<6<20<8<11<8<8<36<1210/08/15<6<6<15<6<14<7<12<6<7<31<610/22/15<7<7<17<8<15<7<13<7<7<32<511/05/15<6<7<18<7<16<7<11<5<7<29<712/03/15(1)MEAN-----------(1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION Table C-IX.1CONCENTRATIONS OF GAMMA EMITTERS IN VEGETATION SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/KG WET +/- 2 SIGMASITECOLLECTIONMn-54Co-58Fe-59Co-60Zn-65Nb-95Zr-95Cs-134Cs-137Ba-140La-140PERIODBD-CONTROLSweet potatoes09/24/15<23<21<60<21<63<24<39<19<22<121<44Swiss chard09/24/15<27<27<76<28<63<26<54<21<28<136<28MEAN-----------BD-QUAD 109/24/15(1)09/24/15(1)MEAN-----------BD-QUAD 2 Beets09/24/15<19<19<44<22<42<20<30<17<18<108<35Cauliflower09/24/15<23<23<56<24<62<26<46<22<22<135<36MEAN-----------BD-QUAD 309/24/15(1)09/24/15(1)MEAN-----------BD-QUAD 409/24/15(1)09/24/15(1)MEAN-----------(1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION Table C-X.1QUARTERLY OSLD RESULTS FOR BRAIDWOOD STATION, 2015RESULTS IN UNITS OF MREM/QUARTER +/- 2 STANDARD DEVIATIONSSTATIONMEAN JAN - MAR APR - JUN JUL - SEP OCT - DECCODE+/- 2 S.D.BD-02-120.7+/-3.119.219.721.122.7BD-02-221.2+/-2.319.521.321.722.1BD-03-120.1+/-2.119.120.019.821.6BD-03-221.2+/-3.719.520.820.523.8BD-04-119.6+/-0.719.119.819.819.8BD-04-219.7+/-3.718.022.319.519.0BD-05-121.0+/-3.619.123.019.922.0BD-05-220.6+/-3.418.621.219.922.6BD-06-119.9+/-2.618.421.219.320.8BD-06-219.6+/-2.318.420.518.820.7BD-19-121.3+/-2.420.020.821.622.8BD-19-221.3+/-3.319.422.120.523.1BD-20-121.4+/-3.918.722.921.022.8BD-20-221.6+/-5.218.824.620.122.7BD-21-120.1+/-3.017.920.920.621.0BD-21-220.5+/-3.518.221.819.921.9BD-101-321.4+/-5.518.224.420.322.8BD-101-420.4+/-2.319.221.920.020.5BD-102-119.4+/-3.018.220.918.020.4BD-102-221.1+/-2.819.322.520.821.8BD-103-120.3+/-2.819.219.620.022.3BD-103-220.8+/-2.119.520.622.020.9BD-104-119.7+/-1.318.920.519.719.8BD-104-220.0+/-2.418.520.619.521.2BD-104-324.4+/-2.323.024.124.725.7BD-104-424.9+/-3.322.526.225.325.6BD-105-119.7+/-4.718.717.919.123.2BD-105-220.1+/-2.618.520.219.921.7BD-105-323.2+/-2.322.322.922.724.9BD-105-426.3+/-8.328.131.322.823.0BD-106-118.9+/-5.118.115.919.622.0BD-106-219.1+/-2.917.920.717.920.0BD-107-120.3+/-3.218.321.619.621.5BD-107-219.1+/-1.818.219.418.620.2BD-108-119.4+/-2.418.120.518.620.3BD-108-220.3+/-2.118.820.120.921.2BD-109-122.6+/-3.520.422.722.724.7BD-109-223.6+/-2.822.724.022.225.3BD-110-120.0+/-2.518.419.720.521.3BD-110-219.9+/-4.117.422.419.720.1BD-110-324.1+/-3.626.125.022.222.9BD-110-425.9+/-3.224.728.124.825.8BD-112-119.3+/-0.819.019.819.319.0BD-112-217.1+/-5.117.919.916.813.8 Table C-X.1QUARTERLY OSLD RESULTS FOR BRAIDWOOD STATION, 2015RESULTS IN UNITS OF MREM/QUARTER +/- 2 STANDARD DEVIATIONSSTATIONMEAN JAN - MAR APR - JUN JUL - SEP OCT - DECCODE+/- 2 S.D.BD-114-119.9+/-3.719.321.117.521.5BD-114-219.7+/-2.018.219.820.520.2BD-115-120.5+/-2.719.422.019.221.2BD-115-220.6+/-3.118.822.019.821.8BD-116-121.2+/-3.419.623.620.521.0BD-116-220.7+/-2.319.121.420.621.6BD-201-124.7+/-6.721.025.5(1)27.6BD-201-222.4+/-4.220.023.3(1)23.9BD-202-120.5+/-2.718.721.520.321.5BD-202-220.4+/-3.517.921.921.320.4BD-203-120.6+/-0.620.220.420.720.9BD-203-220.1+/-3.217.721.020.621.0BD-204-119.4+/-2.518.020.818.920.0BD-204-219.6+/-1.918.319.419.920.6BD-205-119.5+/-3.717.321.819.619.3BD-205-218.7+/-3.817.120.317.020.3BD-206-119.6+/-5.016.720.818.522.4BD-206-220.2+/-2.218.620.720.421.1BD-207-119.6+/-2.118.220.019.420.7BD-207-218.3+/-1.717.119.118.718.3BD-208-120.2+/-1.918.820.320.521.0BD-208-220.3+/-3.618.221.319.422.2BD-209-123.9+/-4.320.724.425.424.9BD-209-224.8+/-3.722.226.324.925.9BD-210-122.9+/-2.621.523.422.324.5BD-210-220.2+/-2.518.7(1)20.821.0BD-211-124.6+/-6.220.526.623.827.3BD-211-224.2+/-3.722.123.325.326.2BD-212-320.1+/-1.718.920.919.920.5BD-212-425.2+/-5.121.925.925.128.0BD-213-319.3+/-2.818.320.017.920.8BD-213-419.5+/-3.218.919.018.121.8BD-214-119.5+/-3.318.021.618.419.9BD-214-222.3+/-2.520.423.123.022.6BD-215-120.3+/-3.418.122.120.120.9BD-215-219.3+/-3.118.719.917.421.0BD-216-121.9+/-4.319.322.921.224.3BD-216-223.2+/-4.220.323.623.825.2BD-111A-120.4+/-2.919.522.519.919.6BD-111A-219.6+/-2.818.418.620.021.4BD-113A-120.7+/-3.719.023.319.920.7BD-113A-220.7+/-3.319.821.518.922.5(1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION TABLE C-X.2MEAN QUARTLY OSLD RESULTS FOR THE INNER RING, OUTER RING, OTHERCONTROL AND ISFSI LOCATIONS FOR BRAIDWOOD STATION, 2015RESULTS IN UNITS OF MREM/QUARTER +/- 2 STANDARD DEVIATIONOF THE STATION DATA COLLECTIONINNER RINGOUTER RING OTHER CONTROL ISFSIPERIOD+/- 2 S.D.JAN-MAR18.9+/-1.919.1+/-3.118.8+/-1.219.3+/-0.624.5+/-4.6APR-JUN21.0+/-3.622.0+/-4.221.6+/-2.720.4+/-1.126.3+/-6.1JUL-SEP19.8+/-2.520.8+/-4.920.3+/-1.720.2+/-1.023.8+/-2.7OCT-DEC21.1+/-3.822.4+/-5.221.7+/-2.522.7+/-3.124.7+/-2.7TABLE C-X.2MEAN QUARTLY OSLD RESULTS FOR THE INNER RING, OUTER RING, OTHER,CONTROL AND ISFSI LOCATIONS FOR BRAIDWOOD STATION, 2015RESULTS IN UNITS OF MREM/QUARTER +/- 2 STANDARD DEVIATIONLOCATIONSAMPLESPERIODPERIOD PERIOD MEANANALYZEDMINIMUMMAXIMUM +/- 2 S.D.INNER RING 12813.825.320.2+/-3.5OUTER RING 12516.728.021.1+/-5.0OTHER 5617.924.620.6+/-3.1CONTROL 819.123.820.6+/-3.0ISFSI 2422.231.324.8+/-4.4INNER RING STATIONS - BD-101-3, BD-101-4, BD-102-1, BD-102-2, BD-103-1, BD-103-2, BD-104-1, BD-104-2, BD-105-1, BD-105-2, BD-106-1, BD-106-2, BD-107-1, BD-107-2, BD-108-1, BD-108-2, BD-109-1, BD-109-2, BD-110-1, BD-110-2, BD-111A-1, BD-111A-2, BD-112-1, BD-112-2, BD-113A-1, BD-113A-2, BD-114-1, BD-114-2, BD-115-1, BD-115-2, BD-116-1, BD-116-2OUTER RING STATIONS - BD-201-1, BD-201-2, BD-202-1, BD-202-2, BD-203-1, BD-203-2, BD-204-1, BD-204-2, BD-205-1, BD-205-2, BD-206-1, BD-206-2, BD-207-1, BD-207-2, BD-208-1, BD-208-2, BD-209-1, BD-209-2, BD-210-1, BD-210-2, BD-211-1, BD-211-2, BD-212-3, BD-212-4, BD-213-3, BD-213-4, BD-214-1, BD-214-2, BD-215-1, BD-215-2, BD-216-1, BD-216-2OTHER STATIONS - BD-02-1, BD-02-2, BD-04-1, BD-04-2, BD-05-1, BD-05-2, BD-06-1, BD-06-2, BD-19-1, BD-19-2, BD-20-1, BD-20-2, BD-21-1, BD-21-2CONTROL STATIONS - BD-03-1, BD-03-2ISFSI STATIONS - BD-104-3, BD-104-4, BD-105-3, BD-105-4, BD-110-3, BD-110-4 DUE TO VENDOR CHANGE IN 2005, < VALUES ARE LLD VALUES JANUARY THROUGH JUNE 2005 AND MDC VALUESAFTER JUNE 2005FIGURE C-1Surface Water - Gross Beta - Stations BD-10 and BD-25 (C)Collected in the Vicinity of Braidwood Station, 2000 - 20150.02.0 4.0 6.0 8.010.001-01-0001-01-0301-01-0601-01-0901-02-1201-02-15pCi/L BD-10 Kankaee River, Downstream 0.02.0 4.0 6.0 8.010.0 12.0 14.0 16.001-01-0001-01-0301-01-0601-01-0901-02-1201-02-15pCi/L BD-25 (C) Kankakee River, Upstream

FIGURE C-2Surface Water - Gross Beta - Stations BD-38 and BD-40Collected in the Vicinity of Braidwood Station, 2007 - 20150.02.0 4.0 6.0 8.010.0 12.0 14.0 16.010-05-0605-29-0801-21-1009-15-1105-09-1301-01-15pCi/L BD-40 Braidwood Station Cooling Lake 0.02.0 4.0 6.0 8.010.0 12.0 14.001-25-0708-27-0803-30-1010-31-1106-02-1301-03-15pCi/L BD-38 Main Drainage Ditch

GAPS IN DATA ARE DUE TO SAMPLING POINTS BEING FROZEN AT TIME OF COLLECTIONFIGURE C-3Surface Water - Gross Beta - Stations BD-55 and BD-56Collected in the Vicinity of Braidwood Station, 2007 - 20150.02.0 4.0 6.0 8.010.001-25-0708-27-0803-30-1010-31-1106-02-1301-03-15pCi/L BD-56 South Pond Fatlan Site 0.02.0 4.0 6.0 8.010.0 12.0 14.001-25-0708-27-0803-30-1010-31-1106-02-1301-03-15pCi/L BD-55 North Pond Fatlan Site

DUE TO VENDOR CHANGE IN 2005, < VALUES ARE LLD VALUES JANUARY THROUGH JUNE 2005 AND MDC VALUESAFTER JUNE 2005FIGURE C-4Surface Water - Tritium - Stations BD-10 and BD-25 (C)Collected in the Vicinity of Braidwood Station, 2000 - 2015 0 500 1000 1500 2000 2500 300003-25-0003-09-0302-20-0602-03-0901-18-1201-01-15pCi/L BD-10 Kankakee River, Downstream 0 100 200 300 40003-25-0003-09-0302-20-0602-03-0901-18-1201-01-15pCi/L BD-25 (C) Kankakee River, Upstream

FIGURE C-5Surface Water - Tritium - Stations BD-38 and BD-40Collected in the Vicinity of Braidwood Station, 2006 - 2015 0 300 600 900 1200 1500 1800 2100 240003-09-0612-13-0709-17-0906-23-1103-28-1301-01-15pCi/L BD-38 Main Drainage Ditch 0 100 200 300 40007-20-0603-28-0812-05-0908-14-1104-22-1312-30-14pCi/L BD-40 Braidwood Station Cooling Lake

FIGURE C-6Surface Water - Tritium - Stations BD-55 and BD-56Collected in the Vicinity of Braidwood Station, 2007 - 2015 0 50 100 150 200 25003-29-0710-16-0805-06-1011-24-1106-13-1301-01-15pCi/L BD-55 North Pond Fatlan Site 0 50 100 150 200 25003-29-0710-16-0805-06-1011-24-1106-13-1301-01-15pCi/L BD-56 South Pond Fatlan Site

DUE TO VENDOR CHANGE, < VALUES ARE LLD VALUES JANUARY THROUGH JUNE 2005 AND MDC VALUESAFTER JUNE 2005FIGURE C-7Public Water - Gross Beta - Station BD-22Collected in the Vicinity of Braidwood Station, 2000 - 20150.02.0 4.0 6.0 8.010.001-29-0001-23-0301-17-0601-11-0901-06-1212-31-14pCi/L BD-22 Wilmington

DUE TO VENDOR CHANGE, < VALUES ARE LLD VALUES JANUARY THROUGH JUNE 2005 AND MDC VALUESAFTER JUNE 2005FIGURE C-8Public Water - Tritium - Station BD-22Collected in the Vicinity of Braidwood Station, 2000 - 2015 0 400 800 1200 1600 2000 2400 2800 3200 3600 4000 4400 4800 5200 5600 6000 6400 6800 7200 760001-29-0001-23-0301-17-0601-11-0901-06-1212-31-14pCi/L BD-22 Wilmington

DUE TO VENDOR CHANGE IN 2005, < VALUES ARE LLD VALUES JANUARY THROUGH JUNE 2005 AND MDC VALUES AFTER JULY.FIGURE C-9Ground/Well Water - Tritium - Stations BD-13 and BD-34Collected in the Vicinity of Braidwood Station, 2000 - 2015 0 100 200 300 400 50001-07-0001-05-0301-03-0601-01-0912-31-1112-29-14pCi/L BD-13 Braidwood City Hall Well 0 100 200 300 400 500 600 70001-07-0001-05-0301-03-0601-01-0912-31-1112-29-14pCi/L BD-34 Gibson Well

DUE TO VENDOR CHANGE IN 2005, < VALUES ARE LLD VALUES JANUARY THROUGH JUNE 2005 AND MDC VALUES AFTER JULY.FIGURE C-10Ground/Well Water - Tritium - Stations BD-35 and BD-36Collected in the Vicinity of Braidwood Station, 2000 - 2015 0 100 200 300 400 50001-07-0001-05-0301-03-0601-01-0912-31-1112-29-14pCi/L BD-35 Joly Well 0 200 400 600 800 1000 120001-07-0001-05-0301-03-0601-01-0912-31-1112-29-14pCi/L BD-36 Hutton Well

FIGURE C-11Ground/Well Water - Tritium - Station BD-37DUE TO VENDOR CHANGE IN 2005, < VALUES ARE LLD VALUES JANUARY THROUGH JUNE 2005 AND MDC VALUES AFTER JULY.Collected in the Vicinity of Braidwood Station, 2000 - 2015 0 100 200 300 400 500 60001-07-0001-05-0301-03-0601-01-0912-31-1112-29-14pCi/L BD-37 Nurczyk Well

NEW STATIONS BD-50 AND BD-51 ADDED IN 2007STATION BD-50 WAS INITIALLY DISCONTINUED ON 10/18/07 AND RESUMED ON 04/08/10FIGURE C-12Ground/Well Water - Tritium - Station BD-50 and BD-51Collected in the Vicinity of Braidwood Station, 2007 - 2015 0 100 200 300 400 500 600 700 800 900 100001-01-0708-07-0803-14-1010-19-1105-25-1312-30-14pCi/L BD-50 Skole Well 0 100 200 300 400 500 60001-03-0708-09-0803-16-1010-21-1105-27-1301-01-15pCi/L BD-51 Fatlan Well

BD-53 was removed from the program during the 3rd quarter of 2011FIGURE C-13Ground/Well Water - Tritium - Stations BD-53 and BD-54Collected in the Vicinity of Braidwood Station, 2007 - 2015 0 100 200 300 400 500 60001-03-0711-03-0709-02-0807-03-0905-03-1003-03-1101-01-12pCi/L BD-53 Phelps Well 0 100 200 300 400 500 60001-03-0708-09-0803-16-1010-21-1105-27-1301-01-15pCi/L BD-54 Cash Well

FIGURE C-14Air Particulate - Gross Beta- Stations BD-03 (C) and BD-06Collected in the Vicinity of Braidwood Station, 2000 - 20150.020.040.0 60.0 80.001-07-0001-06-0301-05-0601-04-0901-04-1201-03-15 10E-03 pCi/m3 BD-03 (C) County Line Road 0.010.020.0 30.0 40.0 50.0 60.001-07-0001-06-0301-05-0601-04-0901-04-1201-03-15 10E-03 pCi/m3 BD-06 Godley FIGURE C-15Air Particulate - Gross Beta- Stations BD-19 and BD-20Collected in the Vicinity of Braidwood Station, 2000 - 20150.010.020.0 30.0 40.0 50.0 60.0 70.001-07-0001-06-0301-05-0601-04-0901-04-1201-03-15 10E-03 pCi/m3 BD-20 Near Field, N 0.010.020.0 30.0 40.0 50.0 60.001-07-0001-06-0301-05-0601-04-0901-04-1201-03-15 10E-03 pCi/m3 BD-19 Near Field, NW

FIGURE C-16Air Particulate - Gross Beta- Station BD-21Collected in the Vicinity of Braidwood Station, 2000 - 20150.010.020.0 30.0 40.0 50.0 60.0 70.001-07-0001-06-0301-05-0601-04-0901-04-1201-03-15 10E-03 pCi/m3 BD-21 Near Field, NE

FIGURE C-17Air Particulate - Gross Beta- Stations BD-02 and BD-04Collected in the Vicinity of Braidwood Station, 2005 - 20150.010.020.0 30.0 40.0 50.0 60.007-07-0505-31-0704-23-0903-17-1102-07-1301-01-15 10E-03 pCi/m3 BD-04 Near Field, N 0.010.020.0 30.0 40.0 50.0 60.007-07-0505-31-0704-23-0903-17-1102-07-1301-01-15 10E-03 pCi/m3 BD-02 Near Field, NW

FIGURE C-18Air Particulate - Gross Beta- Station BD-05Collected in the Vicinity of Braidwood Station, 2005 - 20150.010.020.0 30.0 40.0 50.0 60.007-07-0505-31-0704-23-0903-17-1102-07-1301-01-15 10E-03 pCi/m3 BD-05 Near Field, NE

Intentionally left blank APPENDIX D

INTER-LABORATORY COMPARISON PROGRAM

Intentionally left blank IdentificationReportedKnownRatio (c)Month/YearNumberMatrixNuclideUnitsValue (a)Value (b)TBE/AnalyticsEvaluation (d)March 2015E11181MilkSr-89pCi/L88.997.20.91 ASr-90pCi/L12.217.40.70 WE11182MilkI-131pCi/L61.365.10.94 ACe-141pCi/L 104 1130.92 ACr-51pCi/L 265 2760.96 ACs-134pCi/L 138 1540.90 ACs-137pCi/L 205 2070.99 ACo-58pCi/L 178 1830.97 AMn-54pCi/L 187 1880.99 AFe-59pCi/L 182 1771.03 AZn-65pCi/L 345 3510.98 ACo-60pCi/L 379 4050.94 AE11184 APCe-141pCi 10785.01.26 WCr-51pCi 261 2241.17 ACs-134pCi74.677.00.97 ACs-137pCi99.6 1020.98 ACo-58pCi99.8 1100.91 AMn-54pCi99.296.91.02 AFe-59pCi 109 1190.92 AZn-65pCi 188 1831.03 ACo-60pCi 200 2011.00 AE11183CharcoalI-131pCi82.985.40.97 AE11185WaterFe-55pCi/L 1950 19001.03 AJune 2015E11234MilkSr-89pCi/L94.992.61.02 ASr-90pCi/L14.312.71.13 AE11238MilkI-131pCi/L93.295.90.97 ACe-141pCi/LNot provided for this studyCr-51pCi/L 349 2761.26 WCs-134pCi/L 165 1631.01 ACs-137pCi/L 143 1251.14 ACo-58pCi/L82.068.41.20 AMn-54pCi/L 113 1011.12 AFe-59pCi/L 184 1511.22 WZn-65pCi/L 269 2481.08 ACo-60pCi/L 208 1931.08 AE11237 APCe-141pCiNot provided for this studyCr-51pCi 323 2331.39N (1)Cs-134pCi 139 1381.01 ACs-137pCi 111 1061.05 ACo-58pCi54.057.80.93 AMn-54pCi96.884.91.14 AFe-59pCi 162 1281.27 WZn-65pCi 198 2100.94 ACo-60pCi 178 1631.09 AE11236CharcoalI-131pCi93.9 801.17 ATELEDYNE BROWN ENGINEERING, 2015(PAGE 1 OF 3)TABLE D-1 ANALYTICS ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM IdentificationReportedKnownRatio (c)Month/YearNumberMatrixNuclideUnitsValue (a)Value (b)TBE/AnalyticsEvaluation (d)June 2015E11238WaterFe-55pCi/L 1890 17901.06 ASeptember 2015E11289MilkSr-89pCi/L95.799.10.97 ASr-90pCi/L15.416.40.94 AE11290MilkI-131pCi/L94.999.90.95 ACe-141pCi/L 228 2131.07 ACr-51pCi/L 499 5380.93 ACs-134pCi/L 208 2120.98 ACs-137pCi/L 270 2551.06 ACo-58pCi/L 275 2631.05 AMn-54pCi/L 320 2901.10 AFe-59pCi/L 255 2261.13 AZn-65pCi/L 392 3531.11 ACo-60pCi/L 350 3301.06 AE11292 APCe-141pCi 10485.11.22 WCr-51pCi 262 2151.22 WCs-134pCi86.184.61.02 ACs-137pCi 93 1020.91 ACo-58pCi 106 1051.01 AMn-54pCi 117 1161.01 AFe-59pCi94.890.21.05 AZn-65pCi 160 1411.13 ACo-60pCi 146 1321.11 AE11291CharcoalI-131pCi85.981.71.05 AE11293WaterFe-55pCi/L 2090 18001.16 AE11294SoilCe-141pCi/kg 209 2220.94 ACr-51pCi/kg 463 5600.83 ACs-134pCi/kg 231 2211.05 ACs-137pCi/kg 311 3440.90 ACo-58pCi/kg 245 2740.89 AMn-54pCi/kg 297 3020.98 AFe-59pCi/kg 248 2351.06 AZn-65pCi/kg 347 3680.94 ACo-60pCi/kg 328 3440.95 ADecember 2015E11354MilkSr-89pCi/L96.286.81.11 ASr-90pCi/L14.812.51.18 AE11355MilkI-131pCi/L95.191.21.04 ACe-141pCi/L 117 1290.91 ACr-51pCi/L 265 2810.94 ACs-134pCi/L 153 1600.96 ACs-137pCi/L 119 1151.03 ACo-58pCi/L 107 1100.97 AMn-54pCi/L 153 1451.06 AFe-59pCi/L 117 1081.08 AZn-65pCi/L 261 2481.05 ACo-60pCi/L 212 2131.00 ATABLE D-1 ANALYTICS ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM(PAGE 2 OF 3)TELEDYNE BROWN ENGINEERING, 2015 IdentificationReportedKnownRatio (c)Month/YearNumberMatrixNuclideUnitsValue (a)Value (b)TBE/AnalyticsEvaluation (d)December 2015E11357 APCe-141pCi89.984.01.07 ACr-51pCi 215 1841.17 ACs-134pCi 103 1050.98 ACs-137pCi76.674.81.02 ACo-58pCi76.271.91.06 AMn-54pCi91.494.40.97 AFe-59pCi78.670.31.12 AZn-65pCi 173 1621.07 ACo-60pCi 138 1390.99 AE11422 APSr-89pCi98.096.91.01 ASr-90pCi10.014.00.71 WE11356CharcoalI-131pCi74.975.21.00 AE11358WaterFe-55pCi/L 2160 17101.26 WE11353SoilCe-141pCi/kg 252 2221.14 ACr-51pCi/kg 485 4851.00 ACs-134pCi/kg 319 2771.15 ACs-137pCi/kg 292 2761.06 ACo-58pCi/kg 193 1901.02 AMn-54pCi/kg 258 2501.03 AFe-59pCi/kg 218 1861.17 AZn-65pCi/kg 457 4291.07 ACo-60pCi/kg 381 3681.04 A(1) AP Cr Cr-51 has the shortest half-life and the weakest gamma energy of the mixed nuclide sample, which produces a large error. Taking into account the error, the lowest value would be 119% of the reference value, which would be considered acceptable. NCR 15-18 (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 QC 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.(PAGE 3 OF 3)TABLE D-1 ANALYTICS ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAMTELEDYNE BROWN ENGINEERING, 2015 IdentificationReportedKnownAcceptanceMonth/YearNumberMediaNuclide*UnitsValue (a)Value (b)RangeEvaluation (c)March 201515-MaW32WaterAm-241Bq/L0.6320.6540.458 - 0.850 ANi-63Bq/L2.5(1)APu-238Bq/L0.02040.0089(2)APu-239/240Bq/L0.90.80.582 - 1.082 A15-MaS32SoilNi-63Bq/kg 392448.0314 - 582 ASr-90Bq/kg 286 653487 - 849N (3)15-RdF32 APSr-90Bq/sample-0.0991(1)AU-234/233Bq/sample0.02110.01550.0109 - 0.0202N (3)U-238Bq/sample0.0950.0990.069 - 0.129 A15-GrF32 APGr-ABq/sample0.4481.770.53 - 3.01N (3)Gr-BBq/sample0.75800.750.38 - 1.13 A15-RdV32VegetationCs-134Bq/sample8.087.325.12 - 9.52 ACs-137Bq/sample11.69.186.43 - 11.93 WCo-57Bq/sample-0.0096(1)ACo-60Bq/sample6.535.553.89 - 7.22 AMn-54Bq/sample0.0058(1)ASr-90Bq/sample0.9991.080.76 - 1.40 AZn-65Bq/sample-0.108(1)ASeptember 201515-MaW33WaterAm-241Bq/L1.0121.0550.739 - 1.372 ANi-63Bq/L11.88.555.99 - 11.12N (4)Pu-238Bq/L0.7270.6810.477 - 0.885 APu-239/240Bq/L0.8300.9000.630 - 1.170 A15-MaS33SoilNi-63Bq/kg 635 682477 - 887 ASr-90Bq/kg 429 425298 - 553 A15-RdF33 APSr-90Bq/sample1.482.181.53 - 2.83N (4)U-234/233Bq/sample0.1430.1430.100 - 0.186 AU-238Bq/sample0.1490.1480.104 - 0.192 A15-GrF33 APGr-ABq/sample0.4970.900.27 - 1.53 AGr-BBq/sample1.341.560.78 - 2.34 A15-RdV33VegetationCs-134Bq/sample6.105.804.06 - 7.54 ACs-137Bq/sample0.0002(1)ACo-57Bq/sample8.016.624.63 - 8.61 WCo-60Bq/sample4.974.563.19 - 5.93 AMn-54Bq/sample8.337.685.38 - 9.98 ASr-90Bq/sample0.3861.300.91 - 1.69N (4)(1) False positive test.Zn-65Bq/sample6.075.463.82 - 7.10 A(2) Sensitivity evaluation.(3) Soil Sr incomplete digestion of the sample resulted in low results; AP U-234/233 - extremely low activity was difficult to quantify AP Gr-A - the MAPEP filter has the activity embedded in the filter. To corrected the low bias, TBE will create an attenuated efficiency for MAPEP samples. NCR 15-13 (4) Water Ni-63 extremely low activity was difficult to quantify; AP & Vegetation Sr-90 was lost during separation, possible from substance added by MAPEP NCR 15-21.

(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 warning, N=not acceptable.TELEDYNE BROWN ENGINEERING, 2015(PAGE 1 OF 1)TABLE D-2 DOE'S MIXED ANALYTE PERFORMANCE EVALUATION PROGRAM (MAPEP)

IdentificationReportedKnownAcceptanceMonth/YearNumberMediaNuclideUnitsValue (a)Value (b)LimitsEvaluation (c)May 2015RAD-101WaterSr-89pCi/L45.263.251.1 - 71.2 N (1)Sr-90pCi/L28.041.930.8 - 48.1 N (1)Ba-133pCi/L80.682.563.9 - 90.8 ACs-134pCi/L71.775.761.8 - 83.3 ACs-137pCi/L 187 189170 - 210 ACo-60pCi/L85.784.576.0 - 95.3 AZn-65pCi/L 197 203183 - 238 AGr-ApCi/L26.142.622.1 - 54.0 AGr-BpCi/L28.832.921.3 - 40.6 AI-131pCi/L23.523.819.7 - 28.3 AU-NatpCi/L6.196.594.99 - 7.83 AH-3pCi/L 3145 32802770 - 3620 ANovember 2015RAD-103WaterSr-89pCi/L40.935.726.7 - 42.5 ASr-90pCi/L29.331.122.7 - 36.1 ABa-133pCi/L31.532.525.9 - 36.7 ACs-134pCi/L59.6562.350.6 - 68.5 ACs-137pCi/L 156 157141 - 175 ACo-60pCi/L70.671.164.0 - 80.7 AZn-65pCi/L 145 126113 - 149 AGr-ApCi/L38.251.626.9 - 64.7 AGr-BpCi/L42.036.624.1 - 44.2 AI-131pCi/L24.826.321.9 - 31.0 AU-NatpCi/L146.9056.245.7 - 62.4 N (2)H-3pCi/L 21100 2130018700 - 23400 A(1) Yield on the high side of our acceptance range indicates possibility of calcium interference. NCR 15-09(2) Technician failed to dilute original sample. If dilulted, the result would have been 57.1, which fell within the acceptance limits. NCR 15-19 (a) Teledyne Brown Engineering reported result.

(b) The ERA 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) 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. TELEDYNE BROWN ENGINEERING, 2015(PAGE 1 OF 1)TABLE D-3 ERA ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM

Intentionally left blank APPENDIX E EFFLUENT DATA

Intentionally left blank i TABLE OF CONTENTS INTRODUCTION

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1

SUMMARY

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2 1.0. EFFLUENTS

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..... 3 1.1. Gaseous Effluents to the Atmosphere

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3 1.2. Liquids Released to Kankakee River

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3 2.0. SOLID RADIOACTIVE WASTE

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....... 3 3.0. DOSE TO MAN

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. 4 3.1. Gaseous Effluent Pathways

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.. 4 3.1.1. Noble Gases

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4 3.1.1.1. Gamma Dose Rates

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4 3.1.1.2. Beta Air and Skin Dose Rate

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.... 4 3.1.2. Radioactive Iodine & Particulate

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5 3.2. Liquid Effluent Pathways

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....... 5 3.3. Assessment of Dose to Member of Public

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6 4.0. SITE METEOROLOGY

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6 ii Table of Contents (cont.) APPENDIX E

-1 DATA TABLES AND FIGURES

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E-1.1 Station Releases Table 1.1-1 Gaseous Effluents Summation of all Releases

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E-1.2 Table 1.2-1 Liquid Effluents Summation of all Releases

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E-1.4 Table 3.1-1 Maximum Doses Resulting from Airborne Releases

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E-1.6 Table 3.2-1 Maximum Doses Resulting from Liquid Effluents .....................

E-1.16 Table 3.3-1 10CFR20 Compliance Assessment

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E-1.26 Table 3.4-1 Maximum Doses Resulting from Airborne Releases Based On Concurrent Meteorological Data

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......... E-1.28 1 INTRODUCTION Braidwood Station, a two

-unit PWR station, is located in Will County, Illinois, fifteen (15) miles south

-southwest of Joliet, Illinois. Each reactor is designed to have a capacity of 3,587 thermal megawatts. Unit No. 1 went critical on May 29, 1987, and Unit No. 2 went critical on March 8, 1988. The station has been designed to keep releases to the environment at levels below those specified in the regulations.

Liquid effluents from Braidwood Station are released to the Kankakee River in controlled batches after radioassay of each batch. Gaseous effluents are released to the atmosphere and are calculated on the basis of analyses of grab samples of noble gases and tritium, 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. Airborne concentrations of noble gases, I

-131, and particulate radioactivity in offsite areas are calculated using effluent and meteorological data.

Carbon-14 concentration in offsite areas is calculated based on industry

-approved methodology for estimation of the amount released and meteorological data.

Environmental monitoring is conducted by sampling at indicator and control (background) locations in the vicinity of Braidwood Station to measure changes in radiation or radioactivity levels that may be attributable to station operations. If significant changes attributable to Braidwood Station are measured, these changes are correlated with effluent releases. An environmental monitoring program is conducted which also includes all potential pathways at the site. Gaseous pathways include ground plane (direct), inhalation, vegetation, meat, and milk.

Liquid pathways include potable water and freshwater fish. The critical pathway for 201 5 gaseous dose was vegetation. The critical pathway for 201 5 liquid dose was fresh water fish

.

2

SUMMARY

Calculations based on gaseous and liquid effluents, Kankakee River Flow and meteorological data indicate that public dose due to radioactive material attributable to Braidwood Station during the period does not exceed regulatory or Offsite Dose Calculation Manual (ODCM) limits.

The maximally exposed individual's total body dose due to gaseous and liquid emissions from licensed activities at Braidwood Station is 5.8 1 E-01 mrem.

The assessment of radiation doses to the public is performed in accordance with the ODCM. The results of these analyses confirm that the station is operating in compliance with 10CFR50 Appendix I, 10CFR20 and 40CFR190.

3 1.0 EFFLUENTS 1.1 Gaseous Effluents to the Atmosphere Measured concentrations of noble gases, radioiodine, carbon-14, tritium, and particulate radioactivity released to the atmosphere during the year, are listed in Table 1.1

-1. A total of 1.21 E-01 curies of fission and activation gases were released with a maximum quarterly average release rate of

4.1 3 E-0 3 µCi/sec for Unit 1 and 4.13 E-0 3 µCi/sec for Unit 2. A total of 1.4 8 E-04 curies of radioiodine were released during the year with a maximum average quarterly release rate of 6.55 E-0 6 µCi/sec for Unit 1 and 1.11 E-05 µCi/sec for Unit 2.

A total of 1.76-0 5 curies of beta-gamma emitters were released as airborne particulate matter with a maximum average release rate of 2.21E-06 µCi/sec for Unit 1 and <LLD µCi/sec for Unit 2. Alpha-emitting radionuclides were below the lower limit of detection (LLD) for the year.

A total of 2.7 4E+0 2 curies of tritium were released with a maximum average quarterly release rate of 4.47E+00 µCi/sec for Unit 1 and 7.92E+00 µCi/sec for Unit 2.

A total of 8.48E+00 curies of C

-14 was released with a maximum average quarterly release rate of 1.41E-01 uCi/sec from Unit 1 and 1.41E-01 uCi/sec from Unit 2. Alpha-emitting radionuclides were less than the LLD for the year. 1.2 Liquids Released to Kankakee River A total of 7.58E+06 liters of radioactive liquid wastes (prior to dilution) containing 1.33 E-0 1 curies (excluding tritium, noble gases and alpha) were discharged from the station. These wastes were released at a maximum quarterly diluted average concentration of 4.30E-0 9 µCi/ml. Alpha-emitting radionuclides were less than the LLD for the year. A total of 3.2 0E+03 curies of tritium were released from the station. Quarterly release activities are given in Table 1.2

-1. 2.0 SOLID RADIOACTIVE WASTE Solid radioactive wastes were shipped by truck to the Envirocare of Utah and 4 Waste Control Specialists disposal facilities and various waste processors. For detail s, refer to the Braidwood Station 201 5 Radioactive Effluent Release Report.

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 total body dose rates are shown in Table 3.

1-1 and were calculated based on measured effluents and average meteorological data. Based on measured effluents and average meteorological data, the maximum total body dose to an individual would be 5.18 E-01 mrem for the year (Table 3.1

-1) with an occupancy or shielding factor of 0.7 used. The maximum total body dose based on measured effluents and concurrent meteorological data would be 6.20 E-01 mrem (Table 3.4

-1). The maximum gamma air dose was 2.45 E-06 mrad (Table 3.1

-1) based on measured effluents a nd average meteorological data and 4.76E-0 1 mrad based on concurrent meteorological date (Table 3.4-1). 3.1.1.2 Beta 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 radiation for the year 5 was 1.1 9 E-0 4 mrem based on concurrent meteorological data (Table 3.4

-1). The maximum offsite beta air dose for the year was 5.28 E-0 6 mrad (Table 3.1

-1) based on measured effluents and average meteorological data and 6.35 E-0 6 mrad based on concurrent meteorological data (Table 3.4

-1). 3.1.2 Radioactive Iodine

& Particulate The human thyroid exhibits a significant capacity to concentrate ingested or inhaled iodine. I

-131 released during routine operation of the station may be made available to man resulting in a dose to the thyroid. C

-14 is also included in this category. C

-14 exhibits a capacity to concentrate in bone.

C-14 is released in gaseous form and is absorbed into vegetation through photosynthesis. The principal pathway s of interest for C-14 are the consumption of vegetation by humans and milk from which animals have ingested C

-14 through the consumption of vegetation. With the inclusion of C-14 i n plant effluent calculations, human dose in this category is primarily driven by the release of C

-14 from the plant.

The hypothetical dose to the maximum exposed individual living near the station via ingestion of milk and vegetation was calculated. The source of milk and vegetation was assumed to be at the nearest site boundary with the cows pastured and vegetation grown from May through October. The maximum dose from radioactive iodine and particulate (including C

-14) to any organ was 2.27E+00 mrem (child/bone) based on measured effluents and average meteorological data and 2.75E+00 mrem based on concurrent meteorological data. The maximum dose from radioactive iodine and particulate (including C

-14) to the whole body was 5.18 E-01 mrem (child) based on measured effluents and average meteorological data

and 6.20 E-01 mrem based on concurrent meteorological data.

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 6 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 Braidwood Offsite Dose Calculation Manual. The maximum whole body dose and any organ dose for the year was 6.32 E-02 mrem (Table 3.2

-1 [child]) and 1.01 E-0 1 mrem, respectively (Table 3.2-1 [adult]). 3.3 Assessment of Dose to Member of Public During the period January to December, 201 5 , Braidwood Station did not exceed the following limits as shown in Table 3.1

-1 and Table 3.2-1 (based on annual average meteorological data), Table 3.4-1 (based on concurrent meteorological data), and Table 3.3-1: The RETS limits on dose or dose commitment to an individual due to radioactive materials in liquid effluents from each reactor unit (1.5 mrem to the whole body or 5 mrem to any organ during any calendar year; 3 mrem to the whole body or 10 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).

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

4.0 SITE METEOROLOGY A summary of the site meteorological measurements taken during each calendar quarter of the year is given in Appendix F. The data are presented as cumulative joint frequency distributions of the wind direction for the 203' level and wind speed class by atmospheric stability class determined from the temperature difference between the 199' and 30' levels. Data recovery 7 for these measurements was 99.2% during 201 5.

Intentionally left blank APPENDIX E-1 DATA TABLES AND FIGURES

Intentionally left blank Table 1.1-1 BRAIDWOOD NUCLEAR POWER STATION ANNUAL EFFLUENT REPORT FOR 2015 GAS RELEASES UNIT 1 (Docket Number 50

-456) SUMMATION OF ALL RELEASES Units 1st Qtr 2nd Qtr 3rd Qtr 4th Qtr Est. Total Error% A. Fission and Activation Gas Releases

1. Total Release Activity Ci 1.22E-03 2.90E-03 3.28E-02 2.73E-02 7.59E+00 2. Average Release Rate Ci/sec 1.57E-04 3.69E-04 4.13E-03 3.43E-03 3. Percent of ODCM Limit - gamma % 1.94E-07 4.63E-07 5.22E-06 3.41E-05 4. Percent of ODCM Limit

- beta % 4.70E-07 1.12E-06 1.27E-05 1.66E-05 B. Iodine Releases

1. Total Iodine Ci 6.84E-07 5.15E-05 <LLD 7.83E-06 3.32E+01 2. Average Release Rate Ci/sec 8.80E-08 6.55E-06 N/A 9.85E-07 3. Percent of ODCM Limit

% 7.70E-07 1.22E-05 N/A 3.65E-06 C. Particulate (> 8 day half

-life) Releases

1. Particulates with half

-lives > 8 days Ci <LLD <LLD <LLD 1.76E-05 1.98E+01 2. Average Release Rate Ci/sec N/A N/A N/A 2.21E-06 3. Percent of ODCM Limit

% N/A N/A N/A 1.24E-06 4. Gross Alpha Radioactivity Ci N/A N/A N/A N/A D. Tritium Releases

1. Total Release Activity Ci 1.79E+01 3.50E+01 3.55E+01 2.36E+01 8.07E+00 2. Average Release Rate Ci/sec 2.30E+00 4.45E+00 4.47E+00 2.97E+00 3. Percent of ODCM Limit

% 5.06E-02 9.92E-02 1.01E-01 6.72E-02 E. Gross Alpha Releases

1. Total Release Activity Ci <LLD <LLD <LLD <LLD 1.98E+01 2. Average Release Rate Ci/sec N/A N/A N/A N/A 3. Percent of ODCM limit

% N/A N/A N/A N/A F. Carbon-14 Releases

1. Total Release Activity Ci 1.10E+00 9.43E-01 1.12E+00 1.12E+00 2. Average Release Rate Ci/sec 1.41E-01 1.20E-01 1.41E-01 1.41E-01 Note: LLD Values are included in Appendix A of this report.

Table 1.1-1 BRAIDWOOD NUCLEAR POWER STATION ANNUAL EFFLUENT REPORT FOR 2015 GAS RELEASES UNIT 2 (Docket Number 50-457) SUMMATION OF ALL RELEASES Units 1st Qtr 2nd Qtr 3rd Qtr 4th Qtr Est. Total Error% A. Fission and Activation Gas Releases

1. Total Activity Released Ci 1.22E-03 2.90E-03 3.28E-02 1.99E-02 7.59E+00 2. Average Release Rate Ci/sec 1.57E-04 3.69E-04 4.13E-03 2.50E-03 3. Percent of ODCM Limit

- gamma % 1.94E-07 4.63E-07 5.22E-06 3.18E-06 4. Percent of ODCM Limit - beta % 4.70E-07 1.12E-06 1.27E-05 7.71E-06 B. Iodine Releases

1. Total Iodine Ci <LLD 1.42E-09 9.42E-09 8.81E-05 3.32E+01 2. Average Release Rate Ci/sec N/A 1.81E-10 1.18E-09 1.11E-05 3. Percent of ODCM Limit

% N/A 6.62E-10 4.42E-09 1.05E-05 C. Particulate (> 8 day half

-life) Releases

1. Particulates with half

-lives > 8 days Ci <LLD <LLD <LLD <LLD 1.98E+01 2. Average Release Rate Ci/sec N/A N/A N/A N/A 3. Percent of OCDM Limit

% N/A N/A N/A N/A 4. Gross Alpha Radioactivity Ci N/A N/A N/A N/A D. Tritium Releases

1. Total Release Activity Ci 2.73E+01 3.83E+01 6.30E+01 3.30E+01 8.07E+00 2. Average Release Rate Ci/sec 3.51E+00 4.87E+00 7.92E+00 4.15E+00 3. Percent of ODCM Limit

% 7.78E-02 1.09E-01 1.79E-01 9.38E-02 E. Gross Alpha Releases

1. Total Release Activity Ci <LLD <LLD <LLD <LLD 1.98E+01 2. Average Release Rate Ci/sec N/A N/A N/A N/A 3. Percent of ODCM Limit

% N/A N/A N/A N/A F. Carbon-14 Releases

1. Total Release Activity Ci 1.10E+00 1.02E+00 1.12E+00 9.52E-01 2. Average Release Rate Ci/sec 1.41E-01 1.30E-01 1.41E-01 1.20E-01 Note: LLD Values are included in Appendix A of this report.

Table 1.2-1 BRAIDWOOD NUCLEAR POWER STATION ANNUAL EFFLUENT REPORT FOR 2015 LIQUID RELEASES UNIT 1 (Docket Number 50

-456) SUMMATION OF ALL RELEASES Units 1st Qtr 2nd Qtr 3rd Qtr 4th Qtr Est. Total Error % A. Fission and Activation Products

1. Total Release Ci 1.89E-02 2.88E-02 7.89E-03 1.07E-02 2.64E+00 2. Average Diluted Concentration Ci/ml 2.07E-09 4.30E-09 1.07E-09 1.35E-09 3. Percent of applicable limit

% * * *

B. Tritium 1. Total Release Ci 2.95E+02 4.60E+02 4.35E+02 4.12E+02 5.85E+00 2. Average Diluted Concentration Ci/ml 3.22E-05 6.87E-05 5.91E-05 5.18E-05 3. % of Limit (1E

-2 Ci/ml) % 3.22E-01 6.87E-01 5.91E-01 5.18E-01 C. Dissolved Noble Gases

1. Total Release Ci <LLD 2.37E-05 <LLD 4.86E-06 2.64E+00 2. Average Diluted Concentration Ci/ml N/A 3.54E-12 N/A 6.11E-13 3. % of Limit (2E

-4 Ci/ml) % N/A 1.77E-06 N/A 3.06E-07 D. Gross Alpha A. Total Release Ci <LLD <LLD <LLD <LLD 1.47E+01 E. Volume of Waste Released (prior to dilution) liters 5.39E+05 1.08E+06 1.08E+06 1.09E+06 F. Volume of Dilution Water liters 9.15E+09 6.70E+09 7.36E+09 7.95E+09 Note: LLD Values are included in Appendix A of this report.

Note: % Limit Values are included in Appendix C of this report.

This limit is equal to 10 times the concentration values in Appendix B, Table 2, Column 2 to 10CFR20.1001

-20.2402, except for Dissolved Noble Gases. The limits for Dissolved Noble Gases are found the Braidwood Station ODCM, Table C

-6 of ODCM Appendix C for Noble Gases.

Table 1.2-1 BRAIDWOOD NUCLEAR POWER STATION ANNUAL EFFLUENT REPORT FOR 2015 LIQUID RELEASES UNIT 2 (Docket Number 50

-457) SUMMATION OF ALL RELEASES Units 1st Qtr 2nd Qtr 3rd Qtr 4th Qtr Est. Total Error % A. Fission and Activation Products

1. Total Release Ci 1.89E-02 2.88E-02 7.89E-03 1.07E-02 2.64E+00 2. Average Diluted Concentration Ci/ml 2.07E-09 4.30E-09 1.07E-09 1.35E-09 3. Percent of applicable limit

% * * *

B. Tritium 1. Total Release Ci 2.95E+02 4.60E+02 4.35E+02 4.12E+02 5.85E+00 2. Average Diluted Concentration Ci/ml 3.22E-05 6.87E-05 5.91E-05 5.18E-05 3. % of Limit (1E

-2 Ci/ml) % 3.22E-01 6.87E-01 5.91E-01 5.18E-01 C. Dissolved Noble Gases

1. Total Activity Released Ci <LLD 2.37E-05 <LLD 4.86E-06 2.64E+00 2. Average Diluted Concentration Ci/ml N/A 3.54E-12 N/A 6.11E-13 3. % of Limit (2E

-4 Ci/ml) % N/A 1.77E-06 N/A 3.06E-07 D. Gross Alpha

1. Total Release Ci <LLD <LLD <LLD <LLD 1.47E+01 E. Volume of Waste Released (prior to dilution) liters 5.39E+05 1.08E+06 1.08E+06 1.09E+06 F. Volume of Dilution Water liters 9.15E+09 6.70E+09 7.36E+09 7.95E+09 Note: LLD Values are included in Appendix A of this report.

Note: % Limit Values are included in Appendix C of this report. *This limit is equal to 10 times the concentration values in Appendix B, Table 2, Column 2 to 10CFR20.1001

-2402, except for Dissolved Noble Gases. The limits for Dissolved Noble Gases are found the Braidwood Station ODCM, Table C

-6 of ODCM Appendix C for Noble Gases.

Table 3.1-1 RETDAS v3.6.3 <BRA> VSSI

GASEOUS RELEASE AND DOSE

SUMMARY

REPORT - BY UNIT (Composite Critical Receptor - Limited Analysis)

Release ID...........: 1 All Gas Release Types Period Start Date....: 01/01/2015 00:00 Period End Date......: 01/01/2016 00:00

Period Duration (min): 5.256E+05 Coefficient Type.....: Historical

Unit.................: 1

RELEASE DATA ============================================================

Total Release Duration (minutes)...................................... 5.644E+05 Total Release Volume (cf)............................................. 8.037E+10 Average Release Flowrate (cfm)........................................ 1.424E+05 Average Period Flowrate (cfm)......................................... 1.529E+05

NUCLIDE DATA ============================================================

Average ECrcent Nuclide uCi uCi/cc Ratio EC

-------- --------- -------- KR-90 0.00E+00 0.00E+00 0.00E+00 1.00E

-09 AR-41 7.36E+03 3.23E

-12 3.23E

-04 1.00E

-08 KR-85M 0.00E+00 0.00E+00 0.00E+00 1.00E

-07 KR-87 0.00E+00 0.00E+00 0.00E+00 2.00E

-08 KR-88 0.00E+00 0.00E+00 0.00E+00 9.00E

-09 XE-131M 0.00E+00 0.00E+00 0.00E+00 2.00E

-06 XE-133 5.68E+04 2.50E

-11 4.99E

-05 5.00E ---------

-------- --------- F&AG 6.42E+04 2.82E

-11 3.73E

-04 I-131 8.02E

-01 3.53E

-16 1.76E

-06 2.00E

-10 I-132 4.60E+01 2.02E

-14 1.01E

-06 2.00E

-08 I-133 1.32E+01 5.80E

-15 5.80E

-06 1.00E ---------

-------- --------- Iodine 6.00E+01 2.64E

-14 8.57E

-06 C-14 4.29E+06 1.88E

-09 6.28E

-01 3.00E ---------

-------- --------- Other 4.29E+06 1.88E

-09 6.28E

-01 H-3 1.12E+08 4.92E

-08 4.92E-01 1.00E ---------

-------- --------- H-3 1.12E+08 4.92E

-08 4.92E

-01 AC-227 0.00E+00 0.00E+00 0.00E+00 1.00E

-15 SN-117M 1.19E+01 5.22E

-15 2.61E

-06 2.00E

-09 CE-141 5.73E+00 2.52E-15 3.15E

-06 8.00E ---------

-------- --------- P>=8 1.76E+01 7.74E

-15 5.76E

-06

Table 3.1-1 RETDAS v3.6.3 <BRA> VSSI

GASEOUS RELEASE AND DOSE

SUMMARY

REPORT - BY UNIT (Composite Critical Receptor - Limited Analysis)

Release ID...........: 1 All Gas Release Types Period Start Date....: 01/01/2015 00:00

Period End Date......: 01/01/2016 00:00 Period Duration (min): 5.256E+05 Coefficient Type.....: Historical

Unit.................: 1

NUCLIDE DATA ============================================================

Average ECrcent Nuclide uCi uCi/cc Ratio EC

-------- --------- -------- ----------

-------- --------- Total 1.16E+08 5.11E

-08 1.12E+00

Table 3.1-1 RETDAS v3.6.3 <BRA> VSSI GASEOUS RELEASE AND DOSE

SUMMARY

REPORT - BY UNIT (Composite Critical Receptor - Limited Analysis)

Release ID...........: 1 All Gas Release Types Period Start Date....: 01/01/2015 00:00 Period End Date......: 01/01/2016 00:00

Period Duration (min): 5.256E+05 Coefficient Type.....: Historical

Unit.................: 1 Receptor.............: 5 Composite Crit. Receptor - IP Distance (meters)....: 0.0 Compass Point........: 0.0

PERIOD DOSE BY AGEGROUP, PATHWAY, ORGAN (mrem) ==========================

Age/Path Bone Liver Thyroid Kidney Lung GI

-Lli Skin TB

-------- -------- -------- -------- -------- -------- -------- -------- AGPD 9.46E

-08 9.46E-08 9.46E-08 9.46E-08 9.46E-08 9.46E-08 0.00E+00 9.46E

-08 AINHL 2.87E

-03 3.50E-03 3.50E-03 3.50E-03 3.50E-03 3.50E-03 0.00E+00 3.50E

-03 AVEG 1.42E

-01 3.36E-02 3.36E-02 3.36E-02 3.36E-02 3.36E-02 0.00E+00 3.36E

-02 AGMILK 4.25E

-03 4.51E-03 4.59E-03 4.51E-03 4.51E-03 4.51E-03 0.00E+00 4.51E

-03 ACMEAT 5.26E

-02 1.13E-02 1.13E-02 1.13E-02 1.13E-02 1.13E-02 0.00E+00 1.13E

-02 ACMILK 5.73E

-02 1.33E-02 1.33E-02 1.33E-02 1.33E-02 1.33E-02 0.00E+00 1.33E

-02 TGPD 9.46E-08 9.46E-08 9.46E-08 9.46E-08 9.46E-08 9.46E-08 0.00E+00 9.46E

-08 TINHL 4.10E

-03 3.75E-03 3.76E-03 3.75E-03 3.75E-03 3.75E-03 0.00E+00 3.75E

-03 TVEG 2.29E

-01 5.20E-02 5.20E-02 5.20E-02 5.20E-02 5.20E-02 0.00E+00 5.20E

-02 TGMILK 7.67E

-03 6.29E-03 6.41E-03 6.29E-03 6.29E-03 6.29E-03 0.00E+00 6.29E

-03 TCMEAT 4.44E

-02 9.33E-03 9.33E-03 9.33E-03 9.33E-03 9.33E-03 0.00E+00 9.33E

-03 TCMILK 1.06E

-01 2.35E-02 2.36E-02 2.35E-02 2.35E-02 2.35E-02 0.00E+00 2.35E

-02 CGPD 9.46E

-08 9.46E-08 9.46E-08 9.4 6E-08 9.46E-08 9.46E-08 0.00E+00 9.46E

-08 CINHL 5.67E

-03 3.70E-03 3.70E-03 3.70E-03 3.70E-03 3.70E-03 0.00E+00 3.70E

-03 CVEG 5.52E

-01 1.20E-01 1.20E-01 1.20E-01 1.20E-01 1.20E-01 0.00E+00 1.20E

-01 CGMILK 2.46E

-01 5.95E-02 5.97E-02 5.95E-02 5.95E-02 5.95E-02 0.00E+00 5.95E

-02 CCMEAT 8.35E

-02 1.73E-02 1.73E-02 1.73E-02 1.73E-02 1.73E-02 0.00E+00 1.73E

-02 CCMILK 2.60E

-01 5.56E-02 5.58E-02 5.56E-02 5.56E-02 5.56E-02 0.00E+00 5.56E

-02 IGPD 9.46E

-08 9.46E-08 9.46E-08 9.46E-08 9.46E-08 9.46E-08 0.00E+00 9.46E

-08 IINHL 4.18E

-03 2.36E-03 2.36E-03 2.36E-03 2.36E-03 2.36E-03 0.00E+00 2.36E

-03 IGMILK 5.10E

-01 1.20E-01 1.21E-01 1.20E-01 1.20E-01 1.20E-01 0.00E+00 1.20E

-01 ICMILK 5.10E

-01 1.14E-01 1.15E-01 1.14E-01 1.14E-01 1.14E-01 0.00E+00 1.14E

-01

PERIOD DOSE BY AGEGROUP, ORGAN (mrem) ===================================

Agegroup Bone Liver Thyroid Kidney Lung GI

-Lli Skin TB

-------- -------- -------- -------- -------- -------- -------- -------- ADULT 2.59E

-01 6.61E-02 6.63E-02 6.61E-02 6.61E-02 6.61E-02 0.00E+00 6.61E

-02 TEEN 3.91E

-01 9.49E-02 9.51E-02 9.49E-02 9.49E-02 9.49E-02 0.00E+00 9.49E

-02 CHILD 1.15E+00 2.56E

-01 2.57E-01 2.56E-01 2.56E-01 2.56E-01 0.00E+00 2.56E

-01 INFANT 1.02E+00 2.37E

-01 2.38E-01 2.37E-01 2.37E-01 2.37E-01 0.00E+00 2.37E

-01

Table 3.1-1 RETDAS v3.6.3 <BRA> VSSI

GASEOUS RELEASE AND DOSE

SUMMARY

REPORT - BY UNIT (Composite Critical Receptor - Limited Analysis)

Release ID...........: 1 All Gas Release Types Period Start Date....: 01/01/2015 00:00

Period End Date......: 01/01/2016 00:00

Period Duration (min): 5.256E+05 Coefficient Type.....: Historical Unit.................: 1 Receptor.............: 5 Composite Crit. Receptor - IP Distance (meters)....: 0.0 Compass Point........: 0.0

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

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

Period Group Organ (mrem) Period Limit of Limit Limit of Limit

------ ------- -------- ------- -------- -------- -------- -------- Strt->End CHILD BONE 1.15E+00 31

-day 2.25E

-01 5.10E+02 3.00E

-01 3.83E+02 Qrtr->End CHILD BONE 1.15E+00 Quarter 5.63E+00 2.04E+01 7.50E+00 1.53E+01 Year->End CHILD BONE 1.15E+00 Annual 1.13E+01 1.02E+01 1.50E+01 7.66E+00

Critical Pathway........: 2 Vegetation (VEG)

Major Contributors......: 0.0 % or greater to total Nuclide Percentage

H-3 0.00E+00 C-14 1.00E+02 I-131 1.11E

-04 I-132 2.91E

-06 I-133 2.69E

-05 CE-141 4.45E

-06

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

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

Period Group Organ (mrem) Period Limit of Limit Limit of Limit

------ ------- -------- ------- -------- -------- -------- -------- Strt->End CHILD TBODY 2.56E

-01 31-day 1.50E

-01 1.71E+02 2.00E

-01 1.28E+02 Qrtr->End CHILD TBODY 2.56E

-01 Quarter 5.25E+00 4.88E+00 7.50E+00 3.42E+00 Year->End CHILD TBODY 2.56E

-01 Annual 1.05E+01 2.44E+00 1.50E+01 1.71E+00

Critical Pathway........: 2 Vegetation (VEG)

Major Contributors......: 0.0 % or greater to total Nuclide Percentage

H-3 9.33E+00 C-14 9.06E+01 I-131 2.85E

-04 I-132 1.29E

-05 I-133 6.01E

-05 CE-141 1.62E

-05

Table 3.1-1 RETDAS v3.6.3 <BRA> VSSI

GASEOUS RELEASE AND DOSE

SUMMARY

REPORT - BY UNIT (Composite Critical Receptor - Limited Analysis)

Release ID...........: 1 All Gas Release Types Period Start Date....: 01/01/2015 00:00

Period End Date......: 01/01/2016 00:00

Period Duration (min): 5.256E+05 Coefficient Type.....: Historical

Unit.................: 1 Receptor.............: 4 Composite Crit. Receptor - NG Distance (meters)....: 0.0 Compass Point........: 0.0

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

Dose Dose Limit Admin Admin %

T.Spec T.Spec %

Period Dose Type (mrad) Period Limit of Limit Limit of Limit

--------- -------- ------- -------- -------- -------- -------- Strt->End Gamma 2.00E

-06 31-day 1.50E

-01 1.33E-03 2.00E-01 9.99E-04 Qrtr->End Gamma 2.00E

-06 Quarter 3.75E+00 5.33E

-05 5.00E+00 4.00E

-05 Year->End Gamma 2.00E

-06 Annual 7.50E+00 2.66E

-05 1.00E+01 2.00E

-05 Major Contributors......: 0.0 % or greater to total Nuclide Percentage

----------

KR-90 0.00E+00 AR-41 7.73E+01 KR-85M 0.00E+00 KR-87 0.00E+00 KR-88 0.00E+00 XE-131M 0.00E+00 XE-133 2.27E+01

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

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

Period Dose Type (mrad) Period Limit of Limit Limit of Limit

--------- -------- ------- -------- -------- -------- -------- Strt->End Beta 3.08E-06 31-day 3.00E

-01 1.03E-03 4.00E-01 7.71E-04 Qrtr->End Beta 3.08E

-06 Quarter 7.50E+00 4.11E

-05 1.00E+01 3.08E

-05 Year->End Beta 3.08E

-06 Annual 1.50E+01 2.06E

-05 2.00E+01 1.54E

-05 Major Contributors......: 0.0 % or greater to total

Nuclide Percentage

KR-90 0.00E+00 AR-41 2.88E+01 KR-85M 0.00E+00 KR-87 0.00E+00 KR-88 0.00E+00 XE-131M 0.00E+00 XE-133 7.12E+01

Table 3.1-1 RETDAS v3.6.3 <BRA> VSSI

GASEOUS RELEASE AND DOSE

SUMMARY

REPORT - BY UNIT (Composite Critical Receptor - Limited Analysis)

Release ID...........: 1 All Gas Release Types Period Start Date....: 01/01/2015 00:00

Period End Date......: 01/01/2016 00:00

Period Duration (min): 5.256E+05 Coefficient Type.....: Historical

Unit.................: 2

RELEASE DATA ============================================================

Total Release Duration (minutes)...................................... 5.541E+05 Total Release Volume (cf)............................................. 6.836E+10 Average Release Flowrate (cfm)........................................ 1.234E+05 Average Period Flowrate (cfm)......................................... 1.301E+05

NUCLIDE DATA ============================================================

Average ECrcent Nuclide uCi uCi/cc Ratio EC

-------- --------- -------- AR-41 0.00E+00 0.00E+00 0.00E+00 1.00E

-08 KR-85M 0.00E+00 0.00E+00 0.00E+00 1.00E

-07 KR-87 0.00E+00 0.00E+00 0.00E+00 2.00E

-08 KR-89 0.00E+00 0.00E+00 0.00E+00 1.00E

-09 XE-131M 0.00E+00 0.00E+00 0.00E+00 2.00E

-06 XE-133 5.68E+04 2.94E

-11 5.87E

-05 5.00E ---------

-------- --------- F&AG 5.68E+04 2.94E

-11 5.8 7E-05 I-131 2.65E

-01 1.37E

-16 6.84E

-07 2.00E

-10 I-132 8.78E+01 4.54E

-14 2.27E

-06 2.00E

-08 I-133 2.45E

-02 1.27E

-17 1.27E

-08 1.00E ---------

-------- --------- Iodine 8.81E+01 4.55E-14 2.96E

-06 C-14 4.19E+06 2.17E

-09 7.22E

-01 3.00E ---------

-------- --------- Other 4.19E+06 2.17E

-09 7.22E

-01 H-3 1.62E+08 8.35E

-08 8.35E

-01 1.00E ---------

-------- --------- H-3 1.62E+08 8.35E

-08 8.35E

-01 AC-227 0.00E+00 0.00E+00 0.00E+00 1.00E ---------

-------- --------- P>=8 0.00E+00 0.00E+00 0.00E+00

-------- --------- Total 1.66E+08 8.57E

-08 1.56E+00

Table 3.1-1 RETDAS v3.6.3 <BRA> VSSI

GASEOUS RELEASE AND DOSE

SUMMARY

REPORT - BY UNIT (Composite Critical Receptor - Limited Analysis)

Release ID...........: 1 All Gas Release Types Period Start Date....: 01/01/2015 00:00

Period End Date......: 01/01/2016 00:00

Period Duration (min): 5.256E+05 Coefficient Type.....: Historical Unit.................: 2

Table 3.1-1 RETDAS v3.6.3 <BRA> VSSI

GASEOUS RELEASE AND DOSE

SUMMARY

REPORT - BY UNIT (Composite Critical Receptor - Limited Analysis)

Release ID...........: 1 All Gas Release Types Period Start Date....: 01/01/2015 00:00

Period End Date......: 01/01/2016 00:00

Period Duration (min): 5.256E+05 Coefficient Type.....: Historical Unit.................: 2 Receptor.............: 5 Composite Crit. Receptor - IP Distance (meters)....: 0.0 Compass Point........: 0.0

PERIOD DOSE BY AGEGROUP, PATHWAY, ORGAN (mrem) ==========================

Age/Path Bone Liver Thyroid Kidney Lung GI

-Lli Skin TB

-------- -------- -------- -------- -------- -------- -------- -------- AGPD 5.93E

-08 5.93E-08 5.93E-08 5.93E-08 5.93E-08 5.93E-08 0.00E+00 5.93E

-08 AINHL 2.81E

-03 4.80E-03 4.80E-03 4.80E-03 4.80E-03 4.80E-03 0.00E+00 4.80E

-03 AVEG 1.38E

-01 3.53E-02 3.53E-02 3.53E-02 3.53E-02 3.53E-02 0.00E+00 3.53E

-02 AGMILK 4.15E

-03 6.11E-03 6.14E-03 6.11E-03 6.11E-03 6.11E-03 0.00E+00 6.11E

-03 ACMEAT 5.14E

-02 1.14E-02 1.14E-02 1.14E-02 1.14E-02 1.14E-02 0.00E+00 1.14E

-02 ACMILK 5.60E

-02 1.38E-02 1.38E-02 1.38E-02 1.38E-02 1.38E-02 0.00E+00 1.38E

-02 TGPD 5.93E

-08 5.93E-08 5.93E-08 5.93E-08 5.93E-08 5.93E-08 0.00E+00 5.93E

-08 TINHL 4.01E

-03 5.06E-03 5.06E-03 5.06E-03 5.06E-03 5.06E-03 0.00E+00 5.06E-03 TVEG 2.24E

-01 5.37E-02 5.37E-02 5.37E-02 5.37E-02 5.37E-02 0.00E+00 5.37E

-02 TGMILK 7.50E

-03 8.37E-03 8.40E-03 8.37E-03 8.37E-03 8.37E-03 0.00E+00 8.37E

-03 TCMEAT 4.34E

-02 9.33E-03 9.33E-03 9.33E-03 9.33E-03 9.33E-03 0.00E+00 9.33E

-03 TCMILK 1.03E

-01 2.40E-02 2.41E-02 2.40E-02 2.40E-02 2.40E-02 0.00E+00 2.40E

-02 CGPD 5.93E

-08 5.93E-08 5.93E-08 5.93E-08 5.93E-08 5.93E-08 0.00E+00 5.93E

-08 CINHL 5.54E

-03 4.85E-03 4.85E-03 4.85E-03 4.85E-03 4.85E-03 0.00E+00 4.85E

-03 CVEG 5.40E

-01 1.22E-01 1.22E-01 1.22E-01 1.22E-01 1.22E-01 0.00E+00 1.22E

-01 CGMILK 2.41E

-01 6.16E-02 6.17E-02 6.16E-02 6.16E-02 6.16E-02 0.00E+00 6.16E

-02 CCMEAT 8.16E

-0 2 1.72E-02 1.72E-02 1.72E-02 1.72E-02 1.72E-02 0.00E+00 1.72E

-02 CCMILK 2.55E

-01 5.61E-02 5.6 2E-02 5.61E-02 5.61E-02 5.61E-02 0.00E+00 5.61E

-02 IGPD 5.93E

-08 5.93E-08 5.93E-08 5.93E-08 5.93E-08 5.93E-08 0.00E+00 5.93E

-08 IINHL 4.09E

-03 3.01E-03 3.01E-03 3.01E-03 3.01E-03 3.01E-03 0.00E+00 3.01E

-03 IGMILK 4.98E

-01 1.23E-01 1.23E-01 1.23E-01 1.23E-01 1.23E-01 0.00E+00 1.23E

-01 ICMILK 4.98E

-01 1.14E-01 1.15E-01 1.14E-01 1.14E-01 1.14E-01 0.00E+00 1.14E

-01

PERIOD DOSE BY AGEGROUP, ORGAN (mrem) ===================================

Agegroup Bone Liver Thyroid Kidney Lung GI-Lli Skin TB

-------- -------- -------- -------- -------- -------- -------- -------- ADULT 2.53E

-01 7.14E-02 7.14E-02 7.14E-02 7.14E-02 7.14E-02 0.00E+00 7.14E

-02 TEEN 3.82E

-01 1.00E-01 1.01E-01 1.00E-01 1.00E-01 1.00E-01 0.00E+00 1.00E-01 CHILD 1.12E+00 2.62E

-01 2.62E-01 2.62E-01 2.62E-01 2.62E-01 0.00E+00 2.62E

-01 INFANT 1.00E+00 2.40E

-01 2.41E-01 2.40E-01 2.40E-01 2.40E-01 0.00E+00 2.40E

-01

Table 3.1-1 RETDAS v3.6.3 <BRA> VSSI GASEOUS RELEASE AND DOSE

SUMMARY

REPORT - BY UNIT (Composite Critical Receptor - Limited Analysis)

Release ID...........: 1 All Gas Release Types Period Start Date....: 01/01/2015 00:00

Period End Date......:

01/01/2016 00:00 Period Duration (min): 5.256E+05 Coefficient Type.....: Historical

Unit.................: 2 Receptor.............: 5 Composite Crit. Receptor - IP Distance (meters)....: 0.0 Compass Point........: 0.0

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

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

Period Group Organ (mrem) Period Limit of Limit Limit of Limit

------ ------- -------- ------- -------- -------- -------- -------- Strt->End CHILD BONE 1.12E+00 31

-day 2.25E

-01 4.99E+02 3.00E

-01 3.74E+02 Qrtr->End CHILD BONE 1.12E+00 Quarter 5.63E+00 2.00E+01 7.50E+00 1.50E+01 Year->End CHILD BONE 1.12E+00 Annual 1.13E+01 9.98E+00 1.50E+01 7.48E+00

Critical Pathway........: 2 Vegetation (VEG)

Major Contributors......: 0.0 % or greater to total Nuclide Percentage

H-3 0.00E+00 C-14 9.98E+01 I-131 3.74E-05 I-132 5.68E

-06 I-133 5.12E

-08

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

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

Period Group Organ (mrem) Period Limit of Limit Limit of Limit

------ ------- -------- ------- -------- -------- -------- -------- Strt->End CHILD TBODY 2.62E

-01 31-day 1.50E

-01 1.74E+02 2.00E

-01 1.31E+02 Qrtr->End CHILD TBODY 2.62E

-01 Quarter 5.25E+00 4.98E+00 7.50E+00 3.49E+00 Year->End CHILD TBODY 2.62E

-01 Annual 1.05E+01 2.49E+00 1.50E+01 1.74E+00

Critical Pathway........: 2 Vegetation (VEG)

Major Contributors......: 0.0 % or greater to total Nuclide Percentage

H-3 1.32E+01 C-14 8.68E+01 I-131 9.22E

-05 I-132 2.41E

-05 I-133 1.09E

-07

Table 3.1-1 RETDAS v3.6.3 <BRA> VSSI

GASEOUS RELEASE AND DOSE

SUMMARY

REPORT - BY UNIT (Composite Critical Receptor - Limited Analysis)

Release ID...........: 1 All Gas Release Types Period Start Date....: 01/01/2015 00:00

Period End Date......: 01/01/2016 00:00 Period Duration (min): 5.256E+05 Coefficient Type.....: Historical

Unit.................: 2 Receptor.............: 4 Composite Crit. Receptor - NG Distance (meters)....: 0.0 Compass Point........: 0.0

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

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

Period Dose Type (mrad) Period Limit of Limit Limit of Limit

--------- -------- ------- -------- -------- -------- -------- Strt->End Gamma 4.53E

-07 31-day 1.50E

-01 3.02E-04 2.00E-01 2.26E-04 Qrtr->End Gamma 4.53E

-07 Quarter 3.75E+00 1.21E

-05 5.00E+00 9.06E

-06 Year->End Gamma 4.53E

-07 Annual 7.50E+00 6.04E

-06 1.00E+01 4.53E-06 Major Contributors......: 0.0 % or greater to total Nuclide Percentage

AR-41 0.00E+00 KR-85M 0.00E+00 KR-87 0.00E+00 KR-89 0.00E+00 XE-131M 0.00E+00 XE-133 1.00E+02

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

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

Period Dose Type (mrad) Period Limit of Limit Limit of Limit

--------- -------- ------- -------- -------- -------- -------- Strt->End Beta 2.20E

-06 31-day 3.00E

-01 7.32E-04 4.00E-01 5.49E-04 Qrtr->End Beta 2.20E

-06 Quarter 7.50E+00 2.93E

-05 1.00E+01 2.20E

-05 Year->End Beta 2.20E

-06 Annual 1.50E+01 1.46E

-05 2.00E+01 1.10E

-05 Major Contributors......: 0.0 % or greater to total Nuclide Percentage

AR-41 0.00E+00 KR-85M 0.00E+00 KR-87 0.00E+00 KR-89 0.00E+00 XE-131M 0.00E+00 XE-133 1.00E+02

Table 3.2-1 RETDAS v3.6.3 <BRA> VSSI

LIQUID RELEASE AND DOSE

SUMMARY

REPORT

(PERIOD BASIS - BY UNIT) ------

Release ID............: 1 All Liquid Release Types Period Start Date.....: 01/01/2015 00:00 Period End Date.......: 01/01/2016 00:00 Period Duration (mins): 5.256E+05 Unit..................: 1

MULTIPLE RELEASE POINT MESSAGE ==========================================

Undiluted and Diluted Flowrate(s) and Concentration(s) cannot be combined.

RELEASE DATA ===========================================================

Total Release Duration (minutes)..................................... 1.755E+06 Total Undiluted Volume Released (gallons)............................ NA Average Undiluted Flowrate (gpm)..................................... NA

Total Dilution Volume (gallons)...................................... NA Average Dilution Flowrate (gpm)...................................... NA

NUCLIDE DATA ============================================================

Nuclide uCi

-------- BE-7 3.18E+01 CO-57 4.26E+00 NB-97 7.55E+02 SN-113 8.58E+00 SB-124 5.36E+02 SB-125 2.54E+04 BA-133 1.89E+00 TE-123M 3.94E+02 CR-51 4.58E+03 MN-54 1.99E+02 FE-59 4.20E+02 CO-58 5.66E+03 CO-60 6.02E+03 ZR-95 1.75E+02 NB-95 3.99E+02 AG-110M 3.28E+02 TE-125M 1.54E+04 TE-132 9.37E+01 I-132 4.17E+01 CS-136 1.62E+00 BA-139 8.57E+00

-------- Gamma 6.04E+04

AR-41 1.89E+01 XE-133 9.68E+00

-------- D&EG 2.86E+01

H-3 1.60E+09

Table 3.2-1 RETDAS v3.6.3 <BRA> VSSI LIQUID RELEASE AND DOSE

SUMMARY

REPORT

(PERIOD BASIS - BY UNIT) ------

Release ID............: 1 All Liquid Release Types Period Start Date.....: 01/01/2015 00:00 Period End Date.......: 01/01/2016 00:00 Period Duration (mins): 5.256E+05

NUCLIDE DATA ============================================================

Nuclide uCi

-------- FE-55 4.54E+03 NI-63 1.42E+03

-------- Beta 1.60E+09

-------- Total 1.60E+09

Table 3.2-1 RETDAS v3.6.3 <BRA> VSSI

LIQUID RELEASE AND DOSE

SUMMARY

REPORT

(PERIOD BASIS - BY UNIT) ------

Release ID............: 1 All Liquid Release Types Period Start Date.....: 01/01/2015 00:00 Period End Date.......: 01/01/2016 00:00 Period Duration (mins): 5.256E+05 Unit..................: 1 Receptor..............: 0 Liquid Receptor

PERIOD DOSE BY AGEGROUP, PATHWAY, ORGAN (mrem) ==========================

Age/Path Bone Liver Thyroid Kidney Lung GI

-Lli Skin TB

-------- -------- -------- -------- -------- -------- -------- -------- APWtr 3.52E

-05 1.93E-02 1.93E-02 1.93E-02 1.93E-02 1.94E-02 0.00E+00 1.93E

-02 AFWFSp 2.46E

-03 8.66E-03 8.33E-03 1.26E-02 8.03E-03 3.09E-02 0.00E+00 8.35E

-03 TPWtr 3.37E

-05 1.36E-02 1.36E-02 1.36E-02 1.36E-02 1.36E-02 0.00E+00 1.36E-02 TFWFSp 2.61E

-03 6.85E-03 6.48E-03 6.19E-03 6.19E-03 2.28E-02 0.00E+00 6.51E

-03 CPWtr 1.02E

-04 2.61E-02 2.61E-02 2.61E-02 2.61E-02 2.61E-02 0.00E+00 2.61E

-02 CFWFSp 3.39E

-03 5.76E-03 5.53E-03 5.13E-03 5.13E-03 1.12E-02 0.00E+00 5.53E

-03 IPWtr 8.84E

-05 2.56E-02 2.56E-02 2.56E-02 2.56E-02 2.56E-02 0.00E+00 2.56E

-02 === PERIOD DOSE BY AGEGROUP, ORGAN (mrem) ======================================

Agegroup Bone Liver Thyroid Kidney Lung GI

-Lli Skin TB

-------- -------- -------- -------- -------- -------- -------- -------- ADULT 2.50E

-03 2.80E-02 2.76E-02 3.19E-02 2.73E-02 5.03E-02 0.00E+00 2.76E

-02 TEEN 2.64E

-03 2.04E-02 2.01E-02 1.98E-02 1.98E-02 3.64E-02 0.00E+00 2.01E

-02 CHILD 3.49E

-03 3.19E-02 3.1 6E-02 3.12E-02 3.12E-02 3.74E-02 0.00E+00 3.16E

-02 INFANT 8.84E

-05 2.56E-02 2.56E-02 2.56E-02 2.56E-02 2.56E-02 0.00E+00 2.56E

-02

Table 3.2-1 RETDAS v3.6.3 <BRA> VSSI

LIQUID RELEASE AND DOSE

SUMMARY

REPORT

(PERIOD BASIS - BY UNIT) ------

Release ID............: 1 All Liquid Release Types Period Start Date.....: 01/01/2015 00:00 Period End Date.......: 01/01/2016 00:00 Period Duration (mins): 5.256E+05 Unit..................: 1 Receptor..............: 0 Liquid Receptor

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

Dose Age Dose Limit Admin Admin % T.Spec T.Spec % Period Group Organ (mrem) Period Limit of Limit Limit of Limit

------ ------- -------- ------- -------- -------- -------- -------- Strt->End ADULT GILLI 5.03E

-02 31-day 1.50E

-01 3.35E+01 2.00E

-01 2.51E+01 Qrtr->End ADULT GILLI 5.03E

-02 Quarter 3.75E+00 1.34E+00 5.00E+00 1.01E+00 Year->End ADULT GILLI 5.03E

-02 Annual 7.50E+00 6.70E

-01 1.00E+01 5.03E

-01 Critical Pathway........: 1 Fresh Water Fish - Sport (FFSP)

Major Contributors......: 0.0 %

or greater to total Nuclide Percentage

H-3 5.43E+01 CR-51 8.28E

-02 MN-54 1.50E

-01 FE-55 6.76E

-02 FE-59 1.95E

-01 CO-58 5.97E

-01 CO-60 1.69E+00 NI-63 3.66E

-02 ZR-95 3.96E

-03 NB-95 3.36E+01 AG-110M 1.18E

-02 TE-125M 8.85E+00 TE-132 4.10E

-01 I-132 9.77E

-06 CS-136 1.27E

-03 BA-139 1.22E

-06 === MAXIMUM PERIOD DOSE TO LIMIT (Tot Body)) ===================================

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

Period Group Organ (mrem) Period Limit of Limit Limit of Limit

------ ------- -------- ------- -------- -------- -------- -------- Strt->End CHILD TBODY 3.16E

-02 31-day 4.50E

-02 7.03E+01 6.00E

-02 5.27E+01 Qrtr->End CHILD TBODY 3.16E

-02 Quarter 1.13E+00 2.81E+00 1.50E+00 2.11E+00 Year->End CHILD TBODY 3.16E

-02 Annual 2.25E+00 1.41E+00 3.00E+00 1.05E+00

Critical Pathway........: 0 Potable Water (PWtr)

Major Contributors......: 0.0 % or greater to total Nuclide Percentage

H-3 9.86E+01 CR-51 5.81E

-04

Table 3.2-1 RETDAS v3.6.3 <BRA> VSSI

LIQUID RELEASE AND DOSE

SUMMARY

REPORT

(PERIOD BASIS - BY UNIT) ------

Release ID............: 1 All Liquid Release Types Period Start Date.....: 01/01/2015 00:00 Period End Date.......: 01/01/2016 00:00 Period Duration (mins): 5.256E+05

Major Contributors......: 0.0 % or greater to total Nuclide Percentage

MN-54 1.61E

-02 FE-55 6.29E

-02 FE-59 4.08E

-02 CO-58 1.19E

-01 CO-60 3.57E

-01 NI-63 1.90E

-01 ZR-95 2.20E

-06 NB-95 5.25E

-03 AG-110M 4.61E

-05 TE-125M 6.60E

-01 TE-132 1.51E

-02 I-132 3.86E

-05 CS-136 9.51E

-03 BA-139 6.19E

-08

Table 3.2-1 RETDAS v3.6.3 <BRA> VSSI

LIQUID RELEASE AND DOSE

SUMMARY

REPORT

(PERIOD BASIS - BY UNIT) ------

Release ID............: 1 All Liquid Release Types Period Start Date.....: 01/01/2015 00:00 Period End Date.......: 01/01/2016 00:00 Period Duration (mins): 5.256E+05 Unit..................: 2

MULTIPLE RELEASE POINT MESSAGE ==========================================

Undiluted and Diluted Flowrate(s) and Concentration(s) cannot be combined.

RELEASE DATA ===========================================================

Total Release Duration (minutes)..................................... 1.755E+06 Total Undiluted Volume Released (gallons)............................ NA Average Undiluted Flowrate (gpm)..................................... NA

Total Dilution Volume (gallons)...................................... NA Average Dilution Flowrate (gpm)...................................... NA

NUCLIDE DATA ============================================================

Nuclide uCi

-------- BE-7 3.18E+01 CO-57 4.26E+00 NB-97 7.55E+02 SN-113 8.58E+00 SB-124 5.36E+02 SB-125 2.54E+04 BA-133 1.89E+00 TE-123M 3.94E+02 CR-51 4.58E+03 MN-54 1.99E+02 FE-59 4.20E+02 CO-58 5.66E+03 CO-60 6.02E+03 ZR-95 1.75E+02 NB-95 3.99E+02 AG-110M 3.28E+02 TE-125M 1.54E+04 TE-132 9.37E+01 I-132 4.17E+01 CS-136 1.62E+00 BA-139 8.57E+00

-------- Gamma 6.04E+04

AR-41 1.89E+01 XE-133 9.68E+00

-------- D&EG 2.86E+01

H-3 1.60E+09

Table 3.2-1 RETDAS v3.6.3 <BRA> VSSI LIQUID RELEASE AND DOSE

SUMMARY

REPORT

(PERIOD BASIS - BY UNIT) ------

Release ID............: 1 All Liquid Release Types Period Start Date.....: 01/01/2015 00:00 Period End Date.......: 01/01/2016 00:00

Period Duration (mins): 5.256E+05

NUCLIDE DATA ============================================================

Nuclide uCi

-------- FE-55 4.54E+03 NI-63 1.42E+03

-------- Beta 1.60E+09

-------- Total 1.60E+09

Table 3.2-1 RETDAS v3.6.3 <BRA> VSSI

LIQUID RELEASE AND DOSE

SUMMARY

REPORT

(PERIOD BASIS - BY UNIT) ------

Release ID............: 1 All Liquid Release Types Period Start Date.....: 01/01/2015 00:00 Period End Date.......: 01/01/2016 00:00 Period Duration (mins): 5.256E+05 Unit..................: 2 Receptor..............: 0 Liquid Receptor

PERIOD DOSE BY AGEGROUP, PATHWAY, ORGAN (mrem) ==========================

Age/Path Bone Liver Thyroid Kidney Lung GI

-Lli Skin TB

-------- -------- -------- -------- -------- -------- -------- -------- APWtr 3.52E

-05 1.93E-02 1.93E-02 1.93E-02 1.93E-02 1.94E-02 0.00E+00 1.93E

-02 AFWFSp 2.46E

-03 8.66E-03 8.33E-03 1.26E-02 8.03E-03 3.09E-02 0.00E+00 8.35E

-03 TPWtr 3.37E

-05 1.36E-02 1.36E-02 1.36E-02 1.36E-02 1.36E-02 0.00E+00 1.36E-02 TFWFSp 2.61E

-03 6.85E-03 6.48E-03 6.19E-03 6.19E-03 2.28E-02 0.00E+00 6.51E

-03 CPWtr 1.02E

-04 2.61E-02 2.61E-02 2.61E-02 2.61E-02 2.61E-02 0.00E+00 2.61E

-02 CFWFSp 3.39E

-03 5.76E-03 5.53E-03 5.13E-03 5.13E-03 1.12E-02 0.00E+00 5.53E

-03 IPWtr 8.84E

-05 2.56E-02 2.56E-02 2.56E-02 2.56E-02 2.56E-02 0.00E+00 2.56E

-02 === PERIOD DOSE BY AGEGROUP, ORGAN (mrem) ======================================

Agegroup Bone Liver Thyroid Kidney Lung GI

-Lli Skin TB

-------- -------- -------- -------- -------- -------- -------- -------- ADULT 2.50E

-03 2.80E-02 2.76E-02 3.19E-02 2.73E-02 5.03E-02 0.00E+00 2.76E

-02 TEEN 2.64E

-03 2.04E-02 2.01E-02 1.98E-02 1.98E-02 3.64E-02 0.00E+00 2.01E

-02 CHILD 3.49E

-03 3.19E-02 3.1 6E-02 3.12E-02 3.12E-02 3.74E-02 0.00E+00 3.16E

-02 INFANT 8.84E

-05 2.56E-02 2.56E-02 2.56E-02 2.56E-02 2.56E-02 0.00E+00 2.56E

-02

Table 3.2-1 RETDAS v3.6.3 <BRA> VSSI

LIQUID RELEASE AND DOSE

SUMMARY

REPORT

(PERIOD BASIS - BY UNIT) ------

Release ID............: 1 All Liquid Release Types Period Start Date.....: 01/01/2015 00:00 Period End Date.......: 01/01/2016 00:00 Period Duration (mins): 5.256E+05 Unit..................: 2 Receptor..............: 0 Liquid Receptor

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

Dose Age Dose Limit Admin Admin % T.Spec T.Spec % Period Group Organ (mrem) Period Limit of Limit Limit of Limit

------ ------- -------- ------- -------- -------- -------- -------- Strt->End ADULT GILLI 5.03E

-02 31-day 1.50E

-01 3.35E+01 2.00E

-01 2.51E+01 Qrtr->End ADULT GILLI 5.03E

-02 Quarter 3.75E+00 1.34E+00 5.00E+00 1.01E+00 Year->End ADULT GILLI 5.03E

-02 Annual 7.50E+00 6.70E

-01 1.00E+01 5.03E

-01 Critical Pathway........: 1 Fresh Water Fish - Sport (FFSP)

Major Contributors......: 0.0 %

or greater to total Nuclide Percentage

H-3 5.43E+01 CR-51 8.28E

-02 MN-54 1.50E

-01 FE-55 6.76E

-02 FE-59 1.95E

-01 CO-58 5.97E

-01 CO-60 1.69E+00 NI-63 3.66E

-02 ZR-95 3.96E

-03 NB-95 3.36E+01 AG-110M 1.18E

-02 TE-125M 8.85E+00 TE-132 4.10E

-01 I-132 9.77E

-06 CS-136 1.27E

-03 BA-139 1.22E

-06 === MAXIMUM PERIOD DOSE TO LIMIT (Tot Body)) ===================================

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

Period Group Organ (mrem) Period Limit of Limit Limit of Limit

------ ------- -------- ------- -------- -------- -------- -------- Strt->End CHILD TBODY 3.16E

-02 31-day 4.50E

-02 7.03E+01 6.00E

-02 5.27E+01 Qrtr->End CHILD TBODY 3.16E

-02 Quarter 1.13E+00 2.81E+00 1.50E+00 2.11E+00 Year->End CHILD TBODY 3.16E

-02 Annual 2.25E+00 1.41E+00 3.00E+00 1.05E+00

Critical Pathway........: 0 Potable Water (PWtr)

Major Contributors......: 0.0 % or greater to total Nuclide Percentage

H-3 9.86E+01 CR-51 5.81E

-04

Table 3.2-1 RETDAS v3.6.3 <BRA> VSSI

LIQUID RELEASE AND DOSE

SUMMARY

REPORT

(PERIOD BASIS - BY UNIT) ------

Release ID............: 1 All Liquid Release Types Period Start Date.....: 01/01/2015 00:00 Period End Date.......: 01/01/2016 00:00 Period Duration (mins): 5.256E+05

Major Contributors......: 0.0 % or greater to total Nuclide Percentage

MN-54 1.61E

-02 FE-55 6.29E

-02 FE-59 4.08E

-02 CO-58 1.19E

-01 CO-60 3.57E

-01 NI-63 1.90E

-01 ZR-95 2.20E

-06 NB-95 5.25E

-03 AG-110M 4.61E

-05 TE-125M 6.60E

-01 TE-132 1.51E

-02 I-132 3.86E

-05 CS-136 9.51E

-03 BA-139 6.19E

-08

Table 3-3.1 Braidwood Nuclear Station Unit 1 10 CFR 20 Compliance Assessment

Period of Assessment: 1/1/15 through 12/31/15 Calculated: 04/19/16

10 CFR 20.1301(a)(1) Compliance

Total Effective Dose Equivalent (TEDE) mrem/year 1.14E+00

10 CFR 20.1301(a)(1) limit mrem/year 100.00

% of limit 1.14%

Compliance Summary

1 st Qtr 2nd Qtr 3 rd Qtr 4 th Qtr Total TEDE (mrem) 2.61E-01 2.97E-01 2.97E-01 2.88E-01 1.14E+00

Table 3-3.1 (cont.)

Braidwood Nuclear Station Unit 2 10 CFR 20 Compliance Assessment

Period of Assessment: 1/1/15 through 12/31/15 Calculated: 04/19/1 6

10 CFR 20.1301(a)(1) Compliance

Total Effective Dose Equivalent (TEDE) mrem/year 1.17E+00 10 CFR 20.1301(a)(1) limit mrem/year 100.00

% of limit 1.17%

Compliance Summary

1 st Qtr 2nd Qtr 3 rd Qtr 4 th Qtr Total TEDE (mrem) 2.71E-01 3.16E-01 3.23E-01 2.65E-01 1.17E+00

Table 3.4-1 The following are the maximum annual calculated cumulative offsite doses resulting from Braidwood Station airborne releases in 20 15 based on concurrent meteorological data:

Unit 1: Dose Maximum Value Sector Affected gamma air (1) 3.870 x10-6 mrad North beta air (2) 3.700 x10-6 mrad North whole body (3) 3.070 x10-1 mrem North skin (4) 4.640 x 10

-6 mrem North organ (5) (child-bone) 1.390 x10+0 mrem North Unit 1 Compliance Status 10 CFR 50 Appendix I Yearly Objective % of Appendix I gamma air 10.0 mrad 0.00E+00 beta air 20.0 mrad 0.00E+00 whole body 5.0 mrem 6.14E+00 skin 15.0 mrem 0.00E+00 organ 15.0 mrem 9.27E+00 Unit 2: Dose Maximum Value Sector Affected gamma air (1) 8.910 x10-7 mrad North beta air (2) 2.650 x10-6 mrad North whole body (3) 3.130 x10-1 mrem North skin (4) 1.460 x10-6 mrem North organ (5) (child-bone) 1.360 x10+0 mrem North Unit 2 Compliance Status 10 CFR 50 Appendix I Yearly Objective % of Appendix I gamma air 10.0 mrad 0.00E+00 beta air 20.0 mrad 0.00E+00 whole body 5.0 mrem 6.26E+00 skin 15.0 mrem 0.00E+00 organ 15.0 mrem 9.07E+00 (1) Gamma Air Dose - GASPAR II, NUREG

-0597 (2) Beta Air Dose - GASPAR II, NUREG

-0597 (3) Whole Body Dose - GASPAR II, NUREG

-0597 (4) Skin Dose - GASPAR II, NUREG

-0597 (5) Inhalation and Food Pathways Dose - GASPAR II, NUREG

-0597

Intentionally left blank APPENDIX F

METEOROLOGICAL DATA

Intentionally left blank Braidwood Generating Station

Period of Record: January - March 2015 Stability Class - Extremely Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 0 0 1 0 0 1

NNE 0 0 4 0 0 0 4

NE 0 0 0 0 0 0 0

ENE 0 1 4 0 0 0 5

E 0 0 1 0 0 0 1

ESE 0 2 3 0 0 0 5

SE 0 0 4 0 0 0 4

SSE 0 0 0 1 0 0 1

S 0 0 0 4 0 0 4

SSW 0 0 0 0 0 0 0

SW 0 0 0 0 0 0 0

WSW 0 0 0 2 0 0 2

W 0 0 5 0 0 0 5 WNW 0 4 10 0 0 0 14 NW 0 5 24 0 0 0 29

NNW 0 0 14 2 3 0 19

Variable 0 0 0 0 0 0 0 Total 0 12 69 10 3 0 94

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: 4

Braidwood Generating Station

Period of Record: January - March 2015 Stability Class - Moderately Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 0 2 0 0 0 2

NNE 0 0 1 0 0 0 1

NE 0 3 5 0 0 0 8

ENE 0 5 0 0 0 0 5

E 0 4 1 0 0 0 5

ESE 0 2 1 0 0 0 3

SE 0 1 1 0 0 0 2

SSE 0 0 2 0 0 0 2

S 0 0 0 1 0 0 1

SSW 0 0 2 0 0 0 2

SW 0 0 0 1 0 0 1

WSW 0 0 1 4 0 0 5

W 0 1 3 0 0 0 4 WNW 0 3 2 2 0 0 7

NW 0 4 5 0 0 0 9

NNW 0 3 6 2 2 0 13

Variable 0 0 0 0 0 0 0 Total 0 26 32 10 2 0 70

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: 4

Braidwood Generating Station

Period of Record: January - March 2015 Stability Class - Slightly Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 0 1 0 0 0 1

NNE 0 0 1 1 0 0 2

NE 0 4 0 0 0 0 4

ENE 0 2 0 0 0 0 2

E 0 1 1 0 0 0 2

ESE 0 4 1 0 0 0 5

SE 0 3 0 0 0 0 3

SSE 0 1 2 0 0 0 3

S 0 2 0 2 0 0 4

SSW 0 1 2 3 0 0 6

SW 0 1 3 2 0 0 6

WSW 0 1 0 1 0 0 2

W 0 6 4 0 0 0 10 WNW 0 2 5 0 0 0 7

NW 0 2 6 0 0 0 8

NNW 0 1 6 3 0 0 10

Variable 0 0 0 0 0 0 0 Total 0 31 32 12 0 0 75

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: 4

Braidwood Generating Station

Period of Record: January - March 2015 Stability Class - Neutral - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 10 9 38 0 0 0 57

NNE 6 8 24 17 0 0 55

NE 13 20 11 1 0 0 45

ENE 21 29 6 0 0 0 56

E 7 13 0 0 0 0 20

ESE 4 17 2 0 0 0 23

SE 2 19 8 0 0 0 29

SSE 5 20 13 4 0 0 42 S 2 14 17 12 3 0 48

SSW 4 12 38 26 3 1 84

SW 2 27 59 12 0 0 100

WSW 2 23 21 3 0 0 49

W 9 36 27 3 0 0 75 WNW 8 24 42 6 0 0 80

NW 8 16 22 2 0 0 48

NNW 6 16 36 10 1 0 69

Variable 1 0 0 0 0 0 1 Total 110 303 364 96 7 1 881

Hours of calm in this stability class: 3 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4

Braidwood Generating Station

Period of Record: January - March 2015 Stability Class - Slightly Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 10 13 4 0 0 0 27

NNE 4 3 0 2 0 0 9

NE 12 9 4 1 0 0 26

ENE 11 20 0 0 0 0 31

E 27 5 0 0 0 0 32

ESE 7 34 2 0 0 0 43

SE 7 19 5 0 0 0 31

SSE 3 31 14 4 0 0 52

S 0 25 32 9 0 0 66

SSW 0 10 40 6 0 0 56

SW 2 20 44 7 0 0 73

WSW 6 37 17 0 0 0 60

W 21 36 19 0 0 0 76 WNW 14 40 9 0 0 0 63 NW 29 34 10 1 0 0 74

NNW 9 35 6 0 0 0 50

Variable 0 0 0 0 0 0 0 Total 162 371 206 30 0 0 769

Hours of calm in this stability class: 7 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4

Braidwood Generating Station

Period of Record: January - March 2015 Stability Class - Moderately Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 2 1 0 0 0 0 3

NNE 3 0 0 0 0 0 3

NE 1 0 0 0 0 0 1

ENE 6 0 0 0 0 0 6

E 20 0 0 0 0 0 20

ESE 6 1 0 0 0 0 7

SE 1 1 0 0 0 0 2

SSE 2 0 0 0 0 0 2

S 1 0 0 0 0 0 1

SSW 2 3 1 0 0 0 6

SW 3 5 4 0 0 0 12

WSW 13 23 1 0 0 0 37

W 13 25 0 0 0 0 38 WNW 18 5 0 0 0 0 23 NW 9 2 0 0 0 0 11

NNW 3 0 1 0 0 0 4

Variable 1 0 0 0 0 0 1 Total 104 66 7 0 0 0 177

Hours of calm in this stability class: 8 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4

Braidwood Generating Station

Period of Record: January - March 2015 Stability Clas s - Extremely Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

N 1 0 0 0 0 0 1

NNE 1 0 0 0 0 0 1

NE 0 0 0 0 0 0 0

ENE 5 0 0 0 0 0 5

E 7 0 0 0 0 0 7

ESE 1 0 0 0 0 0 1

SE 0 0 0 0 0 0 0

SSE 0 0 0 0 0 0 0

S 1 0 0 0 0 0 1

SSW 0 0 1 0 0 0 1

SW 1 3 0 0 0 0 4

WSW 3 4 0 0 0 0 7

W 6 3 0 0 0 0 9 WNW 6 0 0 0 0 0 6

NW 3 0 0 0 0 0 3

NNW 2 0 0 0 0 0 2

Variable 0 0 0 0 0 0 0 Total 37 10 1 0 0 0 48

Hours of calm in this stability class: 23 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4

Braidwood Generating Station

Period of Record: January - March 2015 Stability Class - Extremely Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 0 0 1 0 0 1

NNE 0 0 0 5 0 0 5 NE 0 0 0 0 0 0 0

ENE 0 0 1 2 0 0 3

E 0 1 2 1 0 0 4

ESE 0 0 0 2 1 0 3

SE 0 0 1 3 1 0 5

SSE 0 0 0 0 0 0 0

S 0 0 0 0 4 0 4

SSW 0 0 0 0 1 0 1

SW 0 0 0 0 0 0 0

WSW 0 0 0 0 2 0 2

W 0 0 2 3 0 0 5 WNW 0 0 3 4 4 0 11

NW 0 1 7 21 3 0 32

NNW 0 0 4 9 2 3 18

Variable 0 0 0 0 0 0 0 Total 0 2 20 51 18 3 94

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: 4

Braidwood Generating Station

Period of Record: January - March 2015 Stability Class - Moderately Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 0 2 1 0 0 3

NNE 0 0 0 0 0 0 0

NE 0 1 2 3 0 0 6

ENE 0 3 1 2 0 0 6 E 0 1 2 1 0 0 4

ESE 0 1 0 1 0 0 2

SE 0 0 4 1 0 0 5

SSE 0 0 0 2 0 0 2

S 0 0 0 0 0 0 0

SSW 0 0 2 0 1 0 3

SW 0 0 0 0 1 0 1

WSW 0 1 0 2 3 0 6

W 0 1 0 2 0 0 3 WNW 0 0 4 0 3 0 7 NW 0 1 2 6 2 0 11

NNW 0 1 5 2 2 2 12

Variable 0 0 0 0 0 0 0 Total 0 10 24 23 12 2 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: 4 Braidwood Generating Station

Period of Record: January - March 2015 Stability Class - Slightly Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 0 1 0 0 0 1

NNE 0 0 1 0 1 0 2

NE 0 1 0 0 0 0 1

ENE 0 3 1 0 0 0 4

E 0 1 1 1 0 0 3

ESE 0 1 2 1 0 0 4

SE 0 2 2 0 0 0 4

SSE 0 0 0 2 0 0 2

S 0 1 1 0 0 0 2

SSW 0 0 2 0 2 1 5

SW 0 0 0 6 1 0 7

WSW 0 3 0 1 0 0 4

W 0 1 5 0 1 0 7 WNW 0 3 2 0 4 0 9

NW 0 1 1 8 0 0 10

NNW 0 0 2 5 2 1 10

Variable 0 0 0 0 0 0 0 Total 0 17 21 24 11 2 75

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: 4

Braidwood Generating Station

Period of Record: January - March 2015 Stability Class - Neutral - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 3 7 16 20 1 0 47

NNE 1 8 10 24 11 3 57

NE 4 11 10 9 6 0 40

ENE 5 20 12 10 0 0 47

E 2 19 12 4 0 0 37

ESE 0 6 9 6 0 0 21

SE 2 11 13 8 2 0 36

SSE 2 9 8 7 6 0 32

S 3 7 19 8 9 4 50

SSW 3 5 7 34 13 11 73

SW 4 10 36 38 9 3 100

WSW 0 6 39 18 2 0 65

W 2 25 7 19 6 0 59 WNW 4 12 17 31 18 3 85

NW 3 7 8 25 13 2 58

NNW 2 11 18 32 10 2 75

Variable 1 0 0 0 0 0 1 Total 41 174 241 293 106 28 883

Hours of calm in this stability class: 1 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4

Braidwood Generating Station

Period of Record: January - March 2 015 Stability Class - Slightly Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 1 12 18 4 0 0 35

NNE 2 11 4 0 0 1 18

NE 0 4 5 1 3 0 13

ENE 2 4 14 4 0 0 24

E 6 9 14 0 0 0 29 ESE 0 6 19 7 3 0 35

SE 2 5 34 6 2 0 49

SSE 0 12 14 6 6 0 38

S 0 3 22 29 11 0 65

SSW 0 1 15 41 16 1 74

SW 1 4 24 37 6 1 73

WSW 3 10 16 29 0 0 58

W 2 7 16 24 2 0 51 WNW 0 13 22 28 2 0 65

NW 1 15 25 36 6 0 83 NNW 2 16 29 17 0 0 64

Variable 0 0 0 0 0 0 0 Total 22 132 291 269 57 3 774

Hours of calm in this stability class: 2 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4

Braidwood Generating Station

Period of Record: January - March 2015 Stability Class - Moderately Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 2 2 1 0 0 5

NNE 0 0 2 1 0 0 3

NE 1 1 0 0 0 0 2

ENE 1 1 2 0 0 0 4

E 2 1 3 0 0 0 6

ESE 1 2 9 4 0 0 16

SE 1 6 4 0 0 0 11

SSE 0 2 0 0 0 0 2

S 0 3 0 0 0 0 3

SSW 0 0 1 0 0 0 1

SW 0 7 3 3 1 0 14

WSW 0 4 11 0 0 0 15

W 0 5 17 18 1 0 41 WNW 0 3 8 17 0 0 28

NW 1 3 18 4 0 0 26

NNW 0 0 5 2 0 0 7

Variable 1 0 0 0 0 0 1 Total 8 40 85 50 2 0 185

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: 4 Braidwood Generating Station

Period of Record: January - March 2015 Stability Class - Extremely Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 1 0 0 0 0 1

NNE 0 2 0 0 0 0 2

NE 0 1 0 0 0 0 1

ENE 1 0 0 0 0 0 1

E 3 0 2 0 0 0 5

ESE 1 0 0 2 0 0 3

SE 2 3 1 0 0 0 6

SSE 1 1 0 0 0 0 2

S 0 4 0 0 0 0 4

SSW 3 1 2 0 0 0 6 SW 1 5 2 0 0 0 8

WSW 1 0 1 3 0 0 5

W 2 1 1 4 0 0 8 WNW 1 0 3 3 0 0 7 NW 2 2 4 0 0 0 8

NNW 0 2 1 0 0 0 3

Variable 0 0 0 0 0 0 0 Total 18 23 17 12 0 0 70

Hours of calm in this stability class: 1 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4

Braidwood Generating Station

Period of Record: April - June 2015 Stability Class - Extremely Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 1 0 4 0 0 0 5

NNE 0 3 7 0 0 0 10

NE 0 10 10 0 0 0 20

ENE 0 7 0 0 0 0 7

E 0 3 2 0 0 0 5

ESE 0 5 2 0 0 0 7

SE 0 5 3 0 0 0 8

SSE 0 9 0 0 0 0 9

S 0 4 5 1 0 0 10

SSW 0 3 13 7 0 0 23

SW 0 0 2 3 0 0 5

WSW 0 0 13 5 1 0 19

W 2 1 9 7 2 0 21 WNW 2 3 11 2 0 0 18 NW 4 4 15 1 0 0 24

NNW 1 1 2 1 0 0 5

Variable 0 0 0 0 0 0 0 Total 10 58 98 27 3 0 196

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: 0

Braidwood Generating Station

Period of Record: April - June 2015 Stability Class - Moderately Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 3 2 0 0 0 5

NNE 0 7 8 0 0 0 15

NE 0 12 5 0 0 0 17

ENE 0 7 0 0 0 0 7

E 0 0 2 0 0 0 2

ESE 0 1 0 0 0 0 1

SE 0 3 2 0 0 0 5

SSE 0 3 0 0 0 0 3

S 0 3 4 2 0 0 9

SSW 0 3 3 4 0 0 10

SW 2 3 8 5 0 0 18

WSW 0 4 4 1 1 0 10

W 1 3 2 2 1 0 9 WNW 1 2 3 0 1 0 7

NW 1 1 4 0 0 0 6

NNW 1 1 3 0 0 0 5

Variable 0 0 0 0 0 0 0 Total 6 56 50 14 3 0 129

Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 2 Hours of missing stability measurements in all stability classes: 0

Braidwood Generating Station

Period of Record: April - June 2015 Stability Class - Slightly Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 4 0 0 0 0 4

NNE 1 2 7 0 0 0 10

NE 1 12 5 0 0 0 18

ENE 0 5 2 0 0 0 7

E 0 0 0 0 0 0 0

ESE 0 2 0 0 0 0 2

SE 0 3 3 0 0 0 6

SSE 0 8 2 0 0 0 10

S 0 1 1 1 0 0 3

SSW 0 3 4 2 1 0 10

SW 2 3 11 1 0 0 17

WSW 1 5 5 0 0 0 11

W 2 2 1 2 0 0 7 WNW 2 1 2 0 0 0 5

NW 2 0 2 0 0 0 4

NNW 1 5 1 0 0 0 7

Variable 0 0 0 0 0 0 0 Total 12 56 46 6 1 0 121

Hours of calm in this stability class: 1 Hours of missing wind measurements in this stability class: 1 Hours of missing stability measurements in all stability classes: 0

Braidwood Generating Station

Period of Record: April - June 2015 Stability Class - Neutral - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 8 13 1 0 0 0 22

NNE 15 41 27 12 0 0 95

NE 23 87 31 0 0 0 141

ENE 19 44 15 0 0 0 78

E 5 10 2 0 0 0 17

ESE 4 10 3 0 0 0 17

SE 2 16 5 0 0 0 23

SSE 1 22 16 1 0 0 40 S 3 13 19 12 0 0 47

SSW 4 13 27 17 6 0 67

SW 4 24 42 12 2 0 84

WSW 10 11 15 5 2 0 43

W 6 7 13 18 4 0 48 WNW 12 9 9 3 0 0 33

NW 4 13 3 0 0 0 20

NNW 6 11 4 0 0 0 21

Variable 3 0 0 0 0 0 3 Total 129 344 232 80 14 0 799

Hours of calm in this stability class: 3 Hours of missing wind measurements in this stability class: 16 Hours of missing stability measurements in all stability classes: 0

Braidwood Generating Station

Period of Record: April - June 2015 Stability Class - Slightly Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 14 11 1 0 0 0 26

NNE 9 25 1 0 0 0 35

NE 8 22 1 0 0 0 31

ENE 23 29 1 0 0 0 53

E 14 21 0 0 0 0 35

ESE 14 14 2 0 0 0 30

SE 10 21 0 0 0 0 31

SSE 10 42 16 1 0 0 69

S 5 34 53 6 1 0 99

SSW 4 10 42 14 0 0 70

SW 4 22 34 2 0 0 62

WSW 2 15 12 1 1 0 31

W 10 6 4 2 0 0 22 WNW 7 10 6 1 1 0 25 NW 8 8 2 0 0 0 18

NNW 5 8 1 0 0 0 14

Variable 0 0 0 0 0 0 0 Total 147 298 176 27 3 0 651

Hours of calm in this stability class: 10 Hours of missing wind measurements in this stability class: 13 Hours of missing stability measurements in all stability classes: 0

Braidwood Generating Station

Period of Record: April - June 2015 Stability Class - Moderately Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 6 2 0 0 0 0 8

NNE 1 0 0 0 0 0 1

NE 1 1 0 0 0 0 2

ENE 11 2 0 0 0 0 13

E 8 1 0 0 0 0 9

ESE 13 4 0 0 0 0 17

SE 2 4 0 0 0 0 6

SSE 1 8 1 0 0 0 10

S 1 2 2 0 0 0 5

SSW 7 2 1 0 0 0 10

SW 2 2 0 0 0 0 4

WSW 4 7 0 0 0 0 11

W 20 2 0 0 0 0 22 WNW 7 1 0 0 0 0 8

NW 3 0 0 0 0 0 3

NNW 5 1 0 0 0 0 6

Variable 0 0 0 0 0 0 0 Total 92 39 4 0 0 0 135

Hours of calm in this stability class: 24 Hours of missing wind measurements in this stability class: 1 Hours of missing stability measurements in all stability classes: 0

Braidwood Generating Station

Period of Record: April - June 2015 Stability Clas s - Extremely Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

N 2 0 0 0 0 0 2

NNE 1 0 0 0 0 0 1

NE 0 0 0 0 0 0 0

ENE 2 0 0 0 0 0 2

E 2 1 0 0 0 0 3

ESE 2 1 0 0 0 0 3

SE 0 0 0 0 0 0 0

SSE 2 0 0 0 0 0 2

S 0 0 0 0 0 0 0

SSW 1 0 0 0 0 0 1

SW 0 0 0 0 0 0 0

WSW 8 0 0 0 0 0 8

W 4 0 0 0 0 0 4 WNW 3 0 0 0 0 0 3

NW 7 0 0 0 0 0 7

NNW 2 0 0 0 0 0 2

Variable 0 0 0 0 0 0 0 Total 36 2 0 0 0 0 38

Hours of calm in this stability class: 41 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0

Braidwood Generating Station

Period of Record: April - June 2015 Stability Class - Extremely Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 0 0 3 0 0 3

NNE 0 0 1 6 0 0 7 NE 0 4 4 12 0 0 20

ENE 0 1 5 0 0 0 6

E 0 3 5 0 1 0 9

ESE 0 4 1 1 2 0 8

SE 0 1 4 4 0 0 9

SSE 0 5 2 0 0 0 7

S 0 1 5 2 0 0 8

SSW 0 0 11 6 6 0 23

SW 0 0 2 1 5 0 8

WSW 0 0 3 7 1 1 12

W 0 1 3 9 8 5 26 WNW 0 0 5 7 7 2 21

NW 0 0 7 13 3 0 23

NNW 0 0 2 2 0 0 4

Variable 0 0 0 0 0 0 0 Total 0 20 60 73 33 8 194

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: 0

Braidwood Generating Station

Period of Record: April - June 2015 Stability Class - Moderately Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 3 2 0 0 0 5

NNE 0 2 7 3 0 0 12

NE 0 2 8 5 1 0 16

ENE 0 5 6 0 0 0 11 E 0 0 0 1 1 0 2

ESE 0 0 0 0 0 0 0

SE 0 3 1 2 0 0 6

SSE 0 2 1 0 0 0 3

S 0 2 2 1 2 0 7

SSW 0 0 5 2 3 0 10

SW 0 3 6 5 1 0 15

WSW 0 1 4 7 1 0 13

W 0 2 2 2 1 3 10 WNW 0 1 1 3 2 0 7 NW 0 1 2 3 2 0 8

NNW 0 1 1 1 0 0 3

Variable 0 0 0 0 0 0 0 Total 0 28 48 35 14 3 128

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: 0 Braidwood Generating Station

Period of Record: April - June 2015 Stability Class - Slightly Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 2 1 1 0 0 4

NNE 2 1 1 2 0 0 6

NE 0 2 11 7 0 0 20

ENE 0 2 4 1 0 0 7

E 0 3 0 0 0 0 3

ESE 0 2 0 0 0 0 2

SE 0 2 1 3 0 0 6

SSE 0 5 4 0 1 0 10

S 0 0 2 1 1 0 4

SSW 0 0 3 4 0 2 9

SW 0 0 6 3 1 0 10

WSW 1 1 9 6 0 0 17

W 0 3 2 1 1 1 8 WNW 0 1 1 2 0 0 4

NW 1 0 0 4 0 0 5

NNW 0 4 3 0 0 0 7

Variable 0 0 0 0 0 0 0 Total 4 28 48 35 4 3 122

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: 0

Braidwood Generating Station

Period of Record: April - June 2015 Stability Class - Neutral - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 12 3 1 0 0 16

NNE 2 10 11 16 11 1 51

NE 3 29 81 35 0 0 148

ENE 2 34 48 24 1 0 109

E 1 15 13 6 1 0 36

ESE 0 5 4 8 1 0 18

SE 0 6 7 6 0 0 19

SSE 1 5 12 16 3 1 38

S 1 5 14 15 2 5 42

SSW 0 6 12 13 13 10 54

SW 1 10 33 31 11 7 93

WSW 3 10 18 8 4 1 44

W 0 7 5 11 14 17 54 WNW 3 8 12 9 8 1 41

NW 1 3 8 9 2 0 23

NNW 1 13 6 3 0 0 23

Variable 2 1 0 0 0 0 3 Total 21 179 287 211 71 43 812

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: 0

Braidwood Generating Station

Period of Record: April - June 2 015 Stability Class - Slightly Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 2 16 4 0 0 22

NNE 2 4 18 7 0 0 31

NE 1 5 20 4 0 0 30

ENE 1 12 27 5 0 0 45

E 1 9 28 5 0 0 43 ESE 0 4 14 11 3 0 32

SE 0 5 18 5 0 0 28

SSE 0 6 17 24 4 0 51

S 0 4 29 40 22 4 99

SSW 0 4 10 37 16 3 70

SW 1 4 17 42 14 0 78

WSW 0 6 19 16 1 0 42

W 4 4 10 8 5 1 32 WNW 1 1 10 6 4 1 23

NW 0 7 8 6 1 1 23 NNW 0 2 9 4 0 0 15

Variable 0 0 0 0 0 0 0 Total 11 79 270 224 70 10 664

Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 10 Hours of missing stability measurements in all stability classes: 0

Braidwood Generating Station

Period of Record: April - June 2015 Stability Class - Moderately Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 1 6 1 0 0 8

NNE 0 1 4 0 0 0 5

NE 0 1 1 0 0 0 2

ENE 1 4 4 1 0 0 10

E 2 1 4 1 0 0 8

ESE 0 0 7 3 0 0 10

SE 0 0 8 7 0 0 15

SSE 1 1 1 6 0 0 9

S 0 5 2 5 0 0 12

SSW 1 3 5 0 1 0 10

SW 1 1 3 2 0 0 7

WSW 0 1 3 0 0 0 4

W 1 4 7 3 0 0 15 WNW 0 2 12 2 0 0 16

NW 1 2 7 1 0 0 11

NNW 0 1 5 0 0 0 6

Variable 0 0 0 0 0 0 0 Total 8 28 79 32 1 0 148

Hours of calm in this stability class: 1 Hours of missing wind measurements in this stability class: 11 Hours of missing stability measurements in all stability classes: 0 Braidwood Generating Station

Period of Record: April - June 2015 Stability Class - Extremely Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 5 4 0 0 0 9

NNE 0 3 1 0 0 0 4

NE 0 2 5 0 0 0 7

ENE 0 0 0 0 0 0 0

E 0 2 1 0 0 0 3

ESE 0 1 0 0 0 0 1

SE 0 2 1 0 0 0 3

SSE 0 2 3 0 0 0 5

S 0 2 0 0 0 0 2

SSW 1 3 0 0 0 0 4 SW 1 3 0 0 0 0 4

WSW 4 2 3 2 0 0 11

W 1 2 8 1 0 0 12 WNW 1 2 1 0 0 0 4 NW 0 0 2 0 0 0 2

NNW 0 2 5 0 0 0 7

Variable 0 0 0 0 0 0 0 Total 8 33 34 3 0 0 78

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: 0

Braidwood Generating Station

Period of Record: July - September 2015 Stability Class - Extremely Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 2 1 0 0 0 3

NNE 0 1 0 1 0 0 2

NE 1 3 3 1 0 0 8

ENE 2 8 0 0 0 0 10

E 3 14 0 0 0 0 17

ESE 1 6 0 0 0 0 7

SE 3 5 0 0 0 0 8

SSE 6 12 5 0 0 0 23

S 3 10 19 2 0 0 34

SSW 2 7 13 3 0 0 25

SW 3 3 17 5 0 0 28

WSW 2 7 18 0 0 0 27

W 1 12 16 13 0 0 42 WNW 0 16 11 0 0 0 27 NW 2 11 5 0 0 0 18

NNW 1 8 8 0 0 0 17

Variable 0 0 0 0 0 0 0 Total 30 125 116 25 0 0 296

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: 3

Braidwood Generating Station

Period of Record: July - September 2015 Stability Class - Moderately Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 2 5 0 0 0 7

NNE 1 2 0 1 0 0 4

NE 5 12 2 1 0 0 20

ENE 3 5 0 0 0 0 8

E 3 6 0 0 0 0 9

ESE 6 3 0 0 0 0 9

SE 2 5 0 0 0 0 7

SSE 8 3 2 0 0 0 13

S 4 7 4 0 0 0 15

SSW 1 3 4 2 0 0 10

SW 0 2 0 1 0 0 3

WSW 3 13 4 0 0 0 20

W 2 6 2 1 0 0 11 WNW 1 5 5 0 0 0 11

NW 0 3 1 0 0 0 4

NNW 1 5 2 0 0 0 8

Variable 0 0 0 0 0 0 0 Total 40 82 31 6 0 0 159

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: 3

Braidwood Generating Station

Period of Record: July - September 2015 Stability Class - Slightly Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 1 5 1 0 0 0 7

NNE 4 4 0 0 0 0 8

NE 8 4 2 0 0 0 14

ENE 1 4 0 0 0 0 5

E 3 5 0 0 0 0 8

ESE 1 4 0 0 0 0 5

SE 2 4 0 0 0 0 6

SSE 2 1 0 0 0 0 3

S 1 4 6 0 0 0 11

SSW 1 4 3 2 0 0 10

SW 0 5 4 2 0 0 11

WSW 0 7 1 1 0 0 9

W 1 8 2 0 0 0 11 WNW 0 1 0 0 0 0 1

NW 0 4 0 0 0 0 4

NNW 0 5 0 0 0 0 5

Variable 0 0 0 0 0 0 0 Total 25 69 19 5 0 0 118

Hours of calm in this stability class: 3 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 3

Braidwood Generating Station

Period of Record: July - September 2015 Stability Class - Neutral - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 13 17 3 0 0 0 33

NNE 17 16 15 5 0 0 53

NE 26 17 4 1 0 0 48

ENE 27 11 1 0 0 0 39

E 13 10 0 0 0 0 23

ESE 8 8 0 0 0 0 16

SE 16 21 2 0 0 0 39

SSE 20 17 1 0 0 0 38 S 5 14 19 4 0 0 42

SSW 2 19 17 0 0 0 38

SW 2 18 18 5 0 0 43

WSW 2 15 10 1 0 0 28

W 7 16 4 0 0 0 27 WNW 6 4 4 0 0 0 14

NW 6 8 6 0 0 0 20

NNW 8 13 5 0 0 0 26

Variable 0 0 0 0 0 0 0 Total 178 224 109 16 0 0 527

Hours of calm in this stability class: 11 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 3

Braidwood Generating Station

Period of Record: July - September 2015 Stability Class - Slightly Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 9 15 0 0 0 0 24

NNE 10 13 2 0 0 0 25

NE 11 9 0 0 0 0 20

ENE 47 18 1 0 0 0 66

E 45 4 0 0 0 0 49

ESE 25 8 0 0 0 0 33

SE 16 32 1 0 0 0 49

SSE 25 56 5 0 0 0 86

S 14 64 25 1 0 0 104

SSW 5 40 25 0 0 0 70

SW 5 30 16 0 0 0 51

WSW 9 30 1 0 0 0 40

W 14 11 2 0 0 0 27 WNW 17 7 0 0 0 0 24 NW 15 4 0 0 0 0 19

NNW 15 10 0 0 0 0 25

Variable 0 0 0 0 0 0 0 Total 282 351 78 1 0 0 712

Hours of calm in this stability class: 25 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 3

Braidwood Generating Station

Period of Record: July - September 2015 Stability Class - Moderately Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 2 2 0 0 0 0 4

NNE 8 0 0 0 0 0 8

NE 6 0 0 0 0 0 6

ENE 16 0 0 0 0 0 16

E 28 0 0 0 0 0 28

ESE 14 4 0 0 0 0 18

SE 6 1 0 0 0 0 7

SSE 5 1 0 0 0 0 6

S 3 4 0 0 0 0 7

SSW 1 5 1 0 0 0 7

SW 2 0 0 0 0 0 2

WSW 11 13 0 0 0 0 24

W 21 9 0 0 0 0 30 WNW 13 0 0 0 0 0 13 NW 5 0 0 0 0 0 5

NNW 5 1 0 0 0 0 6

Variable 0 0 0 0 0 0 0 Total 146 40 1 0 0 0 187

Hours of calm in this stability class: 25 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 3

Braidwood Generating Station

Period of Record: July - September 2015 Stability Clas s - Extremely Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

N 3 0 0 0 0 0 3

NNE 3 0 0 0 0 0 3

NE 4 0 0 0 0 0 4

ENE 10 0 0 0 0 0 10

E 12 0 0 0 0 0 12

ESE 7 1 0 0 0 0 8

SE 1 0 0 0 0 0 1

SSE 0 0 0 0 0 0 0

S 0 1 0 0 0 0 1

SSW 0 1 0 0 0 0 1

SW 0 0 0 0 0 0 0

WSW 4 2 0 0 0 0 6

W 16 1 0 0 0 0 17 WNW 16 0 0 0 0 0 16 NW 6 0 0 0 0 0 6

NNW 0 0 0 0 0 0 0

Variable 0 0 0 0 0 0 0 Total 82 6 0 0 0 0 88

Hours of calm in this stability class: 54 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 3

Braidwood Generating Station

Period of Record: July - September 2015 Stability Class - Extremely Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 0 1 0 0 0 1

NNE 0 1 1 0 2 0 4 NE 0 2 1 2 0 0 5

ENE 0 5 2 0 0 0 7

E 0 8 13 0 0 0 21

ESE 1 5 3 0 0 0 9

SE 1 6 2 0 0 0 9

SSE 2 12 4 7 0 0 25

S 0 6 14 13 2 0 35

SSW 1 1 13 5 3 0 23

SW 0 3 11 7 4 0 25

WSW 0 5 15 7 0 0 27

W 0 6 15 8 12 0 41 WNW 0 4 17 9 1 0 31

NW 0 4 8 4 2 0 18

NNW 0 0 9 5 0 0 14

Variable 0 0 0 0 0 0 0 Total 5 68 129 67 26 0 295

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: 3

Braidwood Generating Station

Period of Record: July - September 2015 Stability Class - Moderately Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 0 6 0 0 0 6

NNE 0 0 1 0 1 0 2

NE 0 3 5 5 1 0 14

ENE 1 8 2 2 0 0 13 E 2 8 1 0 0 0 11

ESE 3 5 0 0 0 0 8

SE 1 7 0 0 0 0 8

SSE 1 3 2 2 0 0 8

S 2 5 7 5 2 0 21

SSW 1 2 3 2 0 0 8

SW 1 1 1 0 1 0 4

WSW 0 5 8 2 0 0 15

W 2 7 6 0 1 0 16 WNW 0 1 4 4 1 0 10 NW 0 1 4 1 0 0 6

NNW 1 1 4 1 0 0 7

Variable 0 0 0 0 0 0 0 Total 15 57 54 24 7 0 157

Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 2 Hours of missing stability measurements in all stability classes: 3 Braidwood Generating Station

Period of Record: July - September 2015 Stability Class - Slightly Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 4 3 0 0 0 7

NNE 0 2 2 0 0 0 4

NE 0 7 3 2 0 0 12

ENE 0 7 3 0 0 0 10

E 2 7 1 0 0 0 10

ESE 2 3 1 0 0 0 6

SE 2 6 0 0 0 0 8

SSE 2 1 0 0 0 0 3

S 0 0 7 3 0 0 10

SSW 0 3 1 5 0 0 9

SW 0 6 3 2 1 0 12

WSW 0 4 2 2 1 0 9

W 1 2 5 1 0 0 9 WNW 1 1 1 0 0 0 3

NW 0 0 4 1 0 0 5

NNW 0 1 1 1 0 0 3

Variable 0 0 0 0 0 0 0 Total 10 54 37 17 2 0 120

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: 3

Braidwood Generating Station

Period of Record: July - September 2015 Stability Class - Neutral - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 2 10 19 3 0 0 34

NNE 3 11 8 11 9 0 42

NE 5 15 20 7 3 0 50

ENE 2 13 20 4 0 0 39

E 2 20 10 2 0 0 34

ESE 0 8 8 1 0 0 17

SE 0 10 22 4 0 0 36

SSE 1 7 25 3 0 0 36

S 1 8 15 21 5 0 50

SSW 0 2 19 11 0 0 32

SW 1 7 26 9 6 0 49

WSW 0 5 17 6 0 0 28

W 2 8 8 4 0 0 22 WNW 1 7 4 5 0 0 17

NW 2 8 4 8 1 0 23

NNW 1 11 9 3 0 0 24

Variable 0 0 0 0 0 0 0 Total 23 150 234 102 24 0 533

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: 3

Braidwood Generating Station

Period of Record: July - September 2 015 Stability Class - Slightly Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 1 11 20 3 0 0 35

NNE 1 3 13 4 0 0 21

NE 2 4 18 6 0 0 30

ENE 0 24 19 0 0 0 43

E 0 23 23 3 0 0 49 ESE 1 8 19 1 0 0 29

SE 1 17 33 8 0 0 59

SSE 1 9 23 27 1 0 61

S 1 12 44 59 3 0 119

SSW 1 9 54 27 1 0 92

SW 1 5 43 16 0 0 65

WSW 0 9 17 4 0 0 30

W 3 10 19 4 0 0 36 WNW 3 9 9 3 0 0 24

NW 0 4 6 1 0 0 11 NNW 1 10 16 0 0 0 27

Variable 0 0 0 0 0 0 0 Total 17 167 376 166 5 0 731

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: 3

Braidwood Generating Station

Period of Record: July - September 2015 Stability Class - Moderately Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 1 0 2 1 0 0 4

NNE 0 1 2 0 0 0 3

NE 0 2 5 1 0 0 8

ENE 0 8 2 0 0 0 10

E 0 2 13 2 0 0 17

ESE 0 6 9 8 0 0 23

SE 0 6 7 1 0 0 14

SSE 2 4 5 0 0 0 11

S 1 5 4 0 0 0 10

SSW 0 5 7 2 0 0 14

SW 0 11 3 1 0 0 15

WSW 2 7 10 1 0 0 20

W 2 3 10 10 0 0 25 WNW 0 0 14 4 0 0 18

NW 0 3 6 0 0 0 9

NNW 3 5 3 0 0 0 11

Variable 0 0 0 0 0 0 0 Total 11 68 102 31 0 0 212

Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 3 Braidwood Generating Station

Period of Record: July - September 2015 Stability Class - Extremely Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 2 0 2 0 0 0 4

NNE 1 1 1 0 0 0 3

NE 1 1 0 0 0 0 2

ENE 3 0 0 0 0 0 3

E 3 1 6 1 0 0 11

ESE 3 2 2 6 0 0 13

SE 3 8 3 2 0 0 16

SSE 2 3 0 0 0 0 5

S 5 3 0 1 0 0 9

SSW 6 5 0 0 0 0 11 SW 2 7 1 0 0 0 10

WSW 3 5 1 0 0 0 9

W 1 3 7 3 0 0 14 WNW 2 3 10 0 0 0 15 NW 3 8 1 0 0 0 12

NNW 3 2 0 0 0 0 5

Variable 0 0 0 0 0 0 0 Total 43 52 34 13 0 0 142

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: 3

Braidwood Generating Station

Period of Record: October - December2015 Stability Class - Extremely Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 0 2 0 0 0 2

NNE 0 1 0 0 0 0 1

NE 0 1 0 0 0 0 1

ENE 0 0 0 0 0 0 0

E 0 2 0 0 0 0 2

ESE 0 3 0 0 0 0 3

SE 0 1 1 0 0 0 2

SSE 0 0 1 0 0 0 1

S 0 1 2 2 0 0 5

SSW 0 3 3 5 2 0 13

SW 0 2 4 3 0 0 9

WSW 0 3 2 2 1 0 8

W 0 0 3 1 0 0 4 WNW 0 0 4 3 1 0 8 NW 0 6 9 0 0 0 15

NNW 0 1 5 0 0 0 6

Variable 0 0 0 0 0 0 0 Total 0 24 36 16 4 0 80

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: 29

Braidwood Generating Station

Period of Record: October - December2015 Stability Class - Moderately Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 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 1 0 0 1

NE 0 1 2 0 0 0 3

ENE 0 0 0 0 0 0 0

E 0 0 0 0 0 0 0

ESE 0 1 0 0 0 0 1

SE 0 1 0 1 0 0 2

SSE 0 2 0 1 0 0 3

S 0 1 2 1 0 0 4

SSW 0 3 4 2 0 0 9

SW 0 0 5 2 0 0 7

WSW 0 1 0 1 1 0 3

W 0 1 4 3 0 0 8 WNW 1 1 7 3 1 0 13

NW 0 2 1 0 0 0 3

NNW 0 1 2 0 0 0 3

Variable 0 0 0 0 0 0 0 Total 1 15 27 15 2 0 60

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: 29

Braidwood Generating Station

Period of Record: October - December2015 Stability Class - Slightly Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 2 1 0 0 0 3

NNE 0 1 2 0 0 0 3

NE 0 4 3 2 0 0 9

ENE 0 1 0 0 0 0 1

E 0 0 0 0 0 0 0

ESE 1 1 0 0 0 0 2

SE 0 1 0 1 0 0 2

SSE 0 1 2 0 0 0 3

S 0 4 1 1 0 0 6

SSW 0 0 2 3 0 0 5

SW 0 1 3 0 0 0 4

WSW 0 5 3 0 0 0 8

W 0 0 1 6 1 0 8 WNW 0 3 1 0 0 0 4

NW 0 2 1 0 0 0 3

NNW 0 1 0 0 0 0 1

Variable 0 0 0 0 0 0 0 Total 1 27 20 13 1 0 62

Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 29

Braidwood Generating Station

Period of Record: October - December2015 Stability Class - Neutral - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 3 4 4 0 0 0 11

NNE 3 32 30 6 0 0 71

NE 2 34 36 12 0 0 84

ENE 2 17 13 1 0 0 33

E 2 19 5 0 0 0 26

ESE 1 10 4 0 0 0 15

SE 1 7 28 18 1 0 55

SSE 1 10 26 7 2 0 46 S 1 10 20 27 6 0 64

SSW 1 6 26 19 9 0 61

SW 0 14 35 10 3 0 62

WSW 1 13 34 17 5 1 71

W 4 26 37 18 5 0 90 WNW 2 21 24 9 2 0 58

NW 2 2 7 0 0 0 11

NNW 4 6 10 0 0 0 20

Variable 0 0 0 0 0 0 0 Total 30 231 339 144 33 1 778

Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 9 Hours of missing stability measurements in all stability classes: 29

Braidwood Generating Station

Period of Record: October - December2015 Stability Class - Slightly Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 2 6 11 0 0 0 19

NNE 0 24 9 0 0 0 33

NE 6 9 1 3 0 0 19

ENE 7 27 8 7 0 0 49

E 9 18 0 0 0 0 27

ESE 4 16 7 0 0 0 27

SE 9 23 30 7 0 0 69

SSE 2 57 33 10 0 0 102

S 4 49 88 45 1 0 187

SSW 0 12 43 18 4 0 77

SW 3 30 40 9 1 0 83

WSW 2 35 23 11 0 0 71

W 3 19 21 17 0 0 60 WNW 2 33 13 3 0 0 51 NW 4 5 1 0 0 0 10

NNW 3 15 0 0 0 0 18

Variable 0 0 0 0 0 0 0 Total 60 378 328 130 6 0 902

Hours of calm in this stability class: 1 Hours of missing wind measurements in this stability class: 35 Hours of missing stability measurements in all stability classes: 29

Braidwood Generating Station

Period of Record: October - December2015 Stability Class - Moderately Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 1 0 0 0 0 1

NNE 0 1 0 0 0 0 1

NE 1 0 0 0 0 0 1

ENE 5 0 0 0 0 0 5

E 8 0 0 0 0 0 8

ESE 8 1 0 0 0 0 9

SE 2 2 0 0 0 0 4

SSE 2 5 0 0 0 0 7

S 3 2 0 0 0 0 5

SSW 0 5 10 0 0 0 15

SW 1 5 5 0 0 0 11

WSW 7 9 0 0 0 0 16

W 25 15 0 0 0 0 40 WNW 22 6 0 0 0 0 28 NW 8 0 0 0 0 0 8

NNW 3 0 0 0 0 0 3

Variable 1 0 0 0 0 0 1 Total 96 52 15 0 0 0 163

Hours of calm in this stability class: 4 Hours of missing wind measurements in this stability class: 4 Hours of missing stability measurements in all stability classes: 29

Braidwood Generating Station

Period of Record: October - December2015 Stability Clas s - Extremely Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 34 Feet

Wind Speed (in mph)

Wind Direction 1

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

N 1 0 0 0 0 0 1

NNE 1 0 0 0 0 0 1

NE 2 0 0 0 0 0 2

ENE 3 0 0 0 0 0 3

E 12 0 0 0 0 0 12

ESE 2 0 0 0 0 0 2

SE 0 0 0 0 0 0 0

SSE 0 0 0 0 0 0 0

S 2 0 0 0 0 0 2

SSW 0 1 0 0 0 0 1

SW 0 3 0 0 0 0 3

WSW 4 4 0 0 0 0 8

W 10 5 0 0 0 0 15 WNW 7 0 0 0 0 0 7

NW 2 0 0 0 0 0 2

NNW 1 0 0 0 0 0 1

Variable 0 0 0 0 0 0 0 Total 47 13 0 0 0 0 60

Hours of calm in this stability class: 21 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 29

Braidwood Generating Station

Period of Record: October - December2015 Stability Class - Extremely Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 0 1 0 0 0 1

NNE 0 2 0 0 0 0 2

NE 0 0 0 0 0 0 0

ENE 0 0 0 0 0 0 0

E 0 0 3 0 0 0 3 ESE 0 0 2 0 0 0 2

SE 0 1 1 0 0 0 2

SSE 0 1 0 1 0 0 2

S 0 0 0 1 0 1 2

SSW 0 2 2 1 5 3 13

SW 0 0 2 5 1 0 8

WSW 0 0 3 3 0 0 6

W 0 0 1 2 0 0 3 WNW 0 0 1 4 2 3 10

NW 0 1 7 8 0 0 16

NNW 0 0 2 2 0 0 4

Variable 0 0 0 0 0 0 0 Total 0 7 25 27 8 7 74

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: 29

Braidwood Generating Station

Period of Record: October - December2015 Stability Class - Moderately Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 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 1 0 1

NE 0 0 2 1 0 0 3

ENE 0 0 0 0 0 0 0 E 0 0 0 0 0 0 0

ESE 0 1 0 0 0 0 1

SE 0 1 0 0 0 0 1

SSE 0 1 1 0 1 0 3

S 0 2 1 0 0 0 3

SSW 0 1 1 4 0 1 7

SW 0 0 1 3 1 0 5

WSW 0 0 2 0 2 0 4

W 0 0 1 3 1 0 5 WNW 1 1 0 5 4 2 13 NW 0 2 1 1 0 0 4

NNW 0 0 1 1 0 0 2

Variable 0 0 0 0 0 0 0 Total 1 9 11 18 10 3 52

Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 8 Hours of missing stability measurements in all stability classes: 29 Braidwood Generating Station

Period of Record: October - December2015 Stability Class - Slightly Unstable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 1 2 1 0 0 4

NNE 0 0 0 0 1 0 1

NE 0 4 1 3 1 0 9

ENE 0 0 0 0 0 0 0

E 0 0 1 0 0 0 1

ESE 1 0 1 0 0 0 2

SE 0 1 1 0 0 0 2

SSE 0 0 0 2 0 0 2

S 0 4 1 1 0 0 6

SSW 0 1 1 1 2 1 6

SW 0 1 0 2 0 0 3

WSW 0 4 1 2 0 0 7

W 0 0 1 1 5 0 7 WNW 0 1 1 2 0 0 4

NW 0 1 1 1 0 0 3

NNW 0 1 0 0 0 0 1

Variable 0 0 0 0 0 0 0 Total 1 19 12 16 9 1 58

Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 4 Hours of missing stability measurements in all stability classes: 29

Braidwood Generating Station

Period of Record: October - December2015 Stability Class - Neutral - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 1 5 7 1 1 0 15

NNE 0 22 25 25 12 0 84

NE 0 15 22 29 14 0 80

ENE 2 4 13 4 0 0 23

E 0 3 6 15 3 0 27

ESE 0 1 4 11 0 0 16

SE 0 4 5 12 3 2 26

SSE 0 2 9 13 8 2 34

S 0 2 11 12 16 18 59

SSW 1 4 5 22 13 6 51

SW 1 10 13 17 7 3 51

WSW 1 4 25 21 15 6 72

W 1 12 23 23 14 9 82 WNW 1 4 11 22 17 3 58

NW 3 1 4 5 4 0 17

NNW 1 2 2 9 3 0 17

Variable 0 0 0 0 0 0 0 Total 12 95 185 241 130 49 712

Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 75 Hours of missing stability measurements in all stability classes: 29

Braidwood Generating Station

Period of Record: October - December2 015 Stability Class - Slightly Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 0 1 12 11 2 0 26

NNE 0 2 12 10 2 0 26

NE 0 3 8 11 5 0 27

ENE 1 12 30 5 0 0 48

E 0 3 15 13 0 0 31 ESE 0 3 6 20 2 0 31

SE 1 5 20 25 8 3 62

SSE 1 5 20 23 22 2 73

S 1 5 32 74 54 21 187

SSW 0 9 17 37 11 12 86

SW 0 8 23 27 6 2 66

WSW 1 4 24 15 9 0 53

W 1 2 11 26 17 5 62 WNW 0 0 29 19 9 1 58

NW 0 1 7 4 1 0 13 NNW 1 1 19 1 0 0 22

Variable 0 0 0 0 0 0 0 Total 7 64 285 321 148 46 871

Hours of calm in this stability class: 1 Hours of missing wind measurements in this stability class: 66 Hours of missing stability measurements in all stability classes: 29

Braidwood Generating Station

Period of Record: October - December2015 Stability Class - Moderately Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 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 1 1 0 0 2

NE 0 0 1 0 0 0 1

ENE 0 1 3 0 0 0 4

E 0 2 2 1 0 0 5

ESE 0 0 1 8 0 0 9

SE 0 0 0 1 0 0 1

SSE 0 3 1 0 0 0 4

S 1 3 6 3 0 0 13

SSW 0 3 4 1 0 0 8

SW 0 4 4 10 2 0 20

WSW 0 4 2 3 0 0 9

W 1 1 9 9 0 0 20 WNW 0 3 27 15 0 0 45

NW 0 3 17 1 0 0 21

NNW 0 4 1 0 0 0 5

Variable 0 0 0 0 0 0 0 Total 2 31 79 53 2 0 167

Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 4 Hours of missing stability measurements in all stability classes: 29 Braidwood Generating Station

Period of Record: October - December2015 Stability Class - Extremely Stable - 199Ft-30Ft Delta

-T (F)

Winds Measured at 203 Feet

Wind Speed (in mph)

Wind Direction 1

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

----- ----- ----- ----- ----- ----- -----

N 1 3 0 0 0 0 4

NNE 1 5 0 0 0 0 6

NE 0 2 1 0 0 0 3

ENE 0 3 0 0 0 0 3

E 0 0 1 1 0 0 2

ESE 0 4 0 1 0 0 5

SE 0 0 4 0 0 0 4

SSE 1 7 1 0 0 0 9

S 0 1 0 0 0 0 1

SSW 2 0 0 0 0 0 2 SW 0 1 1 1 0 0 3

WSW 0 1 2 0 0 0 3

W 1 1 3 9 0 0 14 WNW 2 0 4 1 0 0 7 NW 1 3 3 0 0 0 7

NNW 3 2 1 0 0 0 6

Variable 0 0 0 0 0 0 0 Total 12 33 21 13 0 0 79

Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 2 Hours of missing stability measurements in all stability classes: 29

APPENDIX G ERRATA DATA

Intentionally left blank 2015 Errata Data

1. More accurate distances to the ISFSI pad were updated in the ODCM in 2015. The distances reported in the 2014 AREOR were incorrect.

BD-104-3, 0.11 mi E BD-104-4, 0.13 mi E BD-105-3, 0.23 mi SE BD-105-4, 0.20 mi SE BD-110-3, 0.18 mi SE BD-110-4, 0.15 mi SE

2. Page B-3, ISFSI dosimeter locations and directions were updated with the following averaged distances and directions: BD-104-3 and -4, 0.12 mi E BD-105-3 and -4, 0.22 mi SE BD-110-3 and -4, 0.17 mi SE 3. Page B-6, Figure B-1 , Inner Ring and Other OSLD map, was updated to reflect the corrected distances that were included in the 2015 ODCM revision.

Intentionally left blank APPENDIX H ANNUAL RADIOLOGICAL GROUNDWATER PROTECTION PROGRAM REPORT (ARGPPR)

Intentionally left blank BRAIDWOOD STATION UNITS 1 and 2 Annual Radiological Groundwater Protection Program Report

1 January through 31 December 2015 Prepared By May 2016 Braidwood Station Braceville, IL 60407 Docket No:

50-457 50-456 Teledyne Brown Engineering Environmental Services

Intentionally left blank i Table Of Contents I. Summary and Conclusions

................................

..............................

1 II. Introduction

................................

.....................

3 A. Objectives of the RGPP

................................

......................

3 B. Implementation of the Objectives

................................

........ 3 C. Program Description

................................

...........................

4 D. Characteristics of Tritium (H

-3) ................................

................................

...........

4 III. Program Description

................................

...... 5 A. Sample Analysis

................................

.. 5 B. Data Interpretation

................................

...............................

5 C. Background Analysis

................................

...........................

6 1. Background Concentrations of Tritium

................................

.....................

7 IV. Results and Discussion

................................

. 8 A. Missed Samples

................................

.. 8 B. Groundwater Results

................................

...........................

9 C. Surface Water Results

................................

......................

11 D. Drinking Water Well Survey

................................

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11 E. Summary of Results

- Inter-laboratory Comparison Program

..........................

11 F. Leaks, Spills, and Releases

................................

..............

1 1 G. Trends

................................

...............

12 H. Investigations

................................

.... 12 I. Actions Taken

................................

..... 12 ii Appendices Appendix A Location Designation Tables Table A-1 Radiological Groundwater Protection Program

- Sampling Locations, Braidwood Station, 201 5 Figures Figure A-1 Sampling Locations near the Site Boundary of the Braidwood Station , 201 5 Figur e A-2 Intermediate Sampling Locations of the Braidwood Station, 201 5 Figure A-3 Distant Sampling Locations of the Braidwood Station, 201 5 Appendix B Data Tables Tables Table B-I.1 Concentrations of Tritium

, Strontium, Gross Alpha and Gross Beta in Groundwater Samples Collected in the Vicinity of Braidwood Station, 201 5. Table B-I.2 Concentrations of Gamma Emitters in Groundwater Samples Collected in the Vicinity of Braidwood Station, 201 5. Tabl e B-I.3 Concentrations of Hard

-T o-Detects in Groundwater Samples Collected in the Vicinity of Braidwood Station, 201 5. Table B-II.1 Concentrations of Tritium

, Strontium, Gross Alpha and Gross Beta in Surface Water Samples Collected in the Vicinity of Braidwood Station, 201 5. Table B-II.2 Concentrations of Gamma Emitters in Surface Water Samples Collected in the Vicinity of Braidwood Station, 201 5.

I. Summary and Conclusions In 201 5, Exelon continued a comprehensive program that evaluates the impact of station operations on groundwater and surface water in the vicinity of Braidwood Station. This evaluation involved numerous station personnel and contractor support personnel. This report covers groundwater and surface water samples collected from the environment, both on and off station property

, in 201 5. During that time period, 6 19 analyses were performed on 2 1 7 samples from 7 7 locations.

In assessing all the data gathered for this report, it was concluded that the operation of Braidwood Station had no adverse radiological impact on the environment.

Gamma-emitting radionuclides associated with licensed plant operations were not detected at concentrations greater than their respective Lower Limits of Detection (LLDs) as specified in the Offsite Dose Calculation Manual (ODCM) in any of the groundwater or surface water samples. In the case of tritium, Exelon specified that its laboratories achieve a lower limit of detection 10 times less than Braidwood's ODCM and 100 times less than federal regulation.

Strontium-89/90 was not detected at a concentration greater than the LLD of 10.0 and 1.0 picoCuries per liter (pCi/L) respectively in any of the groundwater samples tested.

No tritium was detected in the groundwater or surface water samples at concentrations greater than the United States Environmental Protection Agency (USEPA) drinking water standard (and the Nuclear Regulatory Commission Reporting Limit) of 20,000 pCi/L. Low levels of tritium were detected in groundwater and surface water at concentrations greater than the LLD of 200 pCi/L in 7 9 of 2 17 analyses. The tritium concentrations ranged from 1 8 6 +/- 1 1 2 pCi/L to 3 , 2 0 0 +/- 3 73 pCi/L. The tritium that was detected in the groundwater or surface water is believed to be the result of isolated historical releases and/or background from external sources greater than 200 pCi/L. Gross Alpha and Gross Beta analyses in the dissolved and suspended fractions were performed on groundwater and surface water samples throughout the sampling year in 201 5. Gross Alpha (dissolved) wa s not detected in any groundwater and surface water samples. Gross Alpha (suspended) was detected in two groundwater samples. The concentrations ranged from 1.3 to 3.0 pCi/L. Gross Beta (dissolved) was detected in 4 9 groundwater and surface water samples. The concentrations ranged from 1.

7 to 4 7.1 pCi/L. Gross Beta (suspended) was detected in one groundwater sample. The concentration was 3.6 pCi/L. Hard-To-Detect analyses were performed on one groundwater sample in 2015. The analyses included Am

-241, Cm-242, Cm-243/244, Pu

-238, Pu-239/240, U

-234, U-235 and U-238. Uranium-234 and Uranium

-238 was detected in the sample at concentrations of 0.4 pCi/L and 0.5 pCi/L, respectively. All other hard-to-detect nuclides were not detected at concentrations greater than their respective MDCs.

II. Introduction Braidwood Station, a two

-unit PWR station is located in Will County, Illinois, fifteen (15) miles south

-southwest of Joliet, Illinois. Each reactor is designed to have a capacit y of 3, 587 thermal megawatts. Units No. 1 went critical on May 29, 1987 and Unit No. 2 went critical on March 8, 1988. The station has been designed to keep releases to the environment at levels below those specified in the regulations.

This report covers those analyses performed by Teledyne Brown Engineering (TBE) and Environmental Inc. Midwest Labs (EIML) on samples collected in

201 5.

A. Objective of the Radiological Groundwater Protection Program (RGPP) The long-term objectives of the RGPP are as follows:

1. Identify suitable locations to monitor and evaluate potential impacts from station operations to preclude radiological impact to the environment and potential drinking water sources.

2. Understand the local hydrogeologic regime in the vicinity of the station and maintain up

-to-date knowledge of flow patterns on the surface and shallow subsurface.

3. Perform routine water sampling and radiological analysis of water from selected locations.

4. Report new leaks, spills, or other detections with potential radiological significance to stakeholders in a timely manner

. 5. Regularly assess analytical results to identify adverse trends.

6. Take necessary corrective actions to protect groundwater resources

. B. Implementation of the Objectives The objectives identified have been implemented at Braidwood Station as discussed below:

1. Exelon identified locations to monitor and evaluate d potential impacts from station operations.

2. The Braidwood Station reports describe the local hydrogeologic regime. Periodically, the flow patterns on the surface and shallow subsurface are updated based on ongoing measurements.

3. Braidwood Station will continue to perform routine sampling and radiological analysis of water from selected locations.

4. Braidwood Station has implemented procedures to identify and report new leaks, spills, or other detections with potential radiological significance in a timely manner.

5. Braidwood Station staff and consulting hydrogeologist assess analytical results on an ongoing basis to identify adverse trends.

C. Program Description

1. Sample Collection Sample locations can be found in Table A-1 and Figures A

-1 through A-3, Appendix A.

Groundwater and Surface Water Samples of groundwater and surface water are collected, managed, transported and analyzed in accordance with EPA methods. Sample locations, sample collection frequencies and analytical frequencies are managed in accordance with approv ed station procedures. Contractor and/or station personnel are trained in the collection, preservation management and shipment of samples as well as in documentation of sampling events. Analytical laboratories are subject to internal quality assurance

programs, industry cross

-check programs as well as nuclear industry audits. Station personnel review and evaluate all analytical data as it is received. Additionally, analytical data results are reviewed by an independent hydrogeologist for adverse trends or changes to hydrogeologic conditions.

D. Characteristics of Tritium (H

-3) Tritium is a radioactive isotope of hydrogen. Its chemical properties are the same as hydrog en. Tritiated water behaves the same as ordinary water in both the environment and the body. Tritiated water can be taken into the body by drinking water, breathing air, eating food or absorption through the skin. Once tritiated water enters the body, it disperses quickly and is uniformly distributed. Tritiated water is excreted primarily through urine with a clearance rate characterized by an effective biological half

-life of about 14 days. With such a short biological half

-life, an acute ingestion would be cleared rapidly.

Organically bound tritium (tritium that is incorporated into carbon containing compounds) can remain in the body for a longer period.

Tritium is produced naturally in the upper atmosphere when cosmic rays interact with air molecules. Tritium is also produced during nuclear weapons explosions, as a by

-product in reactors producing electricity and in special production reactors

. Like normal water, tritiated water is colorless and odorless. Tritiated water behaves chemically and physically like non-tritiated water in the subsurface and therefore tritiated water will travel at the same velocity as non tritiated groundwater.

III. Program Description A. Sample Analysis This section describes the general analytical methodologies used by Teledyne Brown Engineering (TBE) and Environmental Incorporated Midwest Laboratory (EIML) to analyze the environmental samples for radioactivity for the Braidwood Station RGPP in 201 5.

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

1. Concentrations of gamma emitters in groundwater and surface water. 2. Concentrations of strontium in groundwater and surface water.

3. Concentrations of tritium in groundwater and surface water.

4. Concentrations of Gross Alpha and Gross Beta (Dissolved and Suspended) in groundwater and surface water. 5. Concentrations of Am

-241 in groundwater.

6. Concentrations of Cm

-242 and Cm

-243/244 in groundwater.

7. Concentrations of Pu

-238 and P u-239/240 in groundwater.

8. Concentrations of U

-234, U-235 and U-238 in groundwater.

9. Concentrations of Fe

-55 in groundwater.

10. Concentrations of Ni

-63 in groundwater.

B. Data Interpretation The radiological data collected prior to Braidwood Station becoming operational were used as a baseline with which these operational data were compared. For the purpose of this report, Braidwood Station was considered operational at initial criticality. Several factors were important in the interpretation of the data: 1. Lower Limit of Detection and Minimum Detectable Concentration The lower limit of detection (LLD) is specified by federal regulation as a minimum sensitivity value that must be achieved routinely by the analytical parameter.

2. Laboratory Measurements Uncertainty The estimated uncertainty in measurement of tritium in environmental samples is frequently on the order of 50% of the measurement value.

Statistically, the exact value of a measurement is expressed as a range with a stated level of confidence. The convention is to report results with a 95% level of confidence. The uncertainty comes from calibration standards, sample volume or weight measurements, sampling uncertainty and other factors. Exelon reports the uncertainty of a measurement created by statistical process (counting error) as well as all sources of error (Total Propagated Uncertainty or TPU). Each result has two values calculated. Exelon reports the TPU by following the result with plus or minus (+/-) the estimated sample standard deviation, as TPU, that is obtained by propagating all sources of analytical uncertainty in measurements.

Analytical uncertainties are reported at the 95% confidence level in this report for reporting consistency with the AREOR.

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

For groundwater and surface water 14 nuclides, Be

-7, K-40, Mn-54, Co-58, Fe-59, Co-60, Zn-65, Nb-95, Zr-95, I-131, Cs-134, Cs-137, Ba-140 and La

-140 were reported.

C. Background Analysis

A pre-operational radiological environmental monitoring program (pre-operational REMP) was conducted to establish background radioactivity levels prior to operation of the Station. The environmental media sampled and analyzed during the pre-operational REMP were atmospheric radiation, fall

-out, domestic water, surface water, marine life and foodstuffs. The results of the monitoring were detailed in the report entitled, Environmental Radiological Monitoring for Braidwood Nuclear Power Station Commonwealth Edison Company, Annual Report 1986, May 1987. 1. Background Concentrations of Tritium The purpose of the following discussion is to summarize background measurements of tritium in various media performed by others.

a. Tritium Production Tritium is created in the environment from naturally occurring processes both cosmic and subterranean, as well as from anthropogenic (i.e., man

-made) sources. In the upper atmosphere, "Cosmogenic" tritium is produced from the bombardment of stable nuclides and combines with oxygen to form tritiated water, which will then enter the hydrologic cycle. Below ground, "lithogenic" tritium is produced by the bombardment of natural lithium present in crystalline rocks by neutrons produced by the radioactive decay of naturally abundant uranium and thorium. Lithogenic production of tritium is usually negligible compared to other sources due to the limited abundance of lithium in rock. The lithogenic tritium is introduced directly to groundwater.

A major anthropogenic source of tritium and strontium

-90 comes from the former atmospheric testing of thermonuclear weapons. Levels of tritium in precipitation increased significantly during the 1950s and early 1 960s and later with additional testing, resulting in the release of significant amounts of tritium to the atmosphere. The Canadian heavy water nuclear power reactors, other commercial power reactors, nuclear research and weapons production continue to influence tritium concentrations in the environment.

b. Precipitation Data

Precipitation samples are routinely collected at stations around the world for the analysis of tritium and other radionuclides. Two publicly available databases that provide tritium concentrations in precipitation are Global Network of Isotopes in Precipitation (GNIP) and USEPA's RadNet database. GNIP provides tritium precipitation concentration data for samples collected world wide from 1960 to 2014. RadNet provides tritium precipitation concentration data for samples collected at stations through out the U.S. from 1960 up to and including 201 5. Based on GNIP data for sample stations located in the U.S. Midwest, tritium concentrations peaked around 1963. This peak, which approached 10,000 pCi/L for some stations, coincided with the atmospheric testing of thermonuclear weapons. Tritium concentrations in surface water showed a sharp decline up until 1975 followed by a gradual decline since that time. Tritium concentrations in Midwest precipitation have typically been below 100 pCi/L since around 1980. Tritium concentrations in wells may still be above the 200 pCi/L detection limit from the external causes described above. Water from previous years and decades is naturally captured in groundwater, so some well water sources today are affected by the surface water from the 1960s that was elevated in tritium.

c. Surface Water Data Tritium concentrations are routinely measured in large surface water bodies, including Lake Michigan and the

Mississippi River. Illinois surface water data were typically less than 100 pCi/L.

The USEPA RadNet surface water data typically has a reported 'Combined Standard Uncertainty' of 35 to 50 pCi/L.

According to USEPA, this corresponds to a

+/- 70 to 100 pCi/L 95% confidence bound on each given measurement. Therefore, the typical background data provided may be subject to measurement uncertainty of approximately

+/- 70 to 100 pCi/L.

The radio-analytical laboratory is counting tritium results to an Exelon specified LLD of 200 pCi/L. Typically, the lowest positive measurement will be reported within a range of 40

- 240 pCi/L or 140 +/- 100 pCi/L. Clearly, these sample results cannot be distinguished as different from background at this concentration.

IV. Results and Discussion

A. Missed Sample

Exelon maintains a RGPP as part of the nuclear industry's voluntary groundwater protection initiative as described in NEI 07-07. As part of this program, samples are obtained routinely from monitoring wells and surface waters at Braidwood based on the frequencies outlined in station procedures.

During the third quarter of 2015, it was discovered that five remediation monitoring wells (VB-1-9D, P-4D, VB-3-4D, P-13D, and VB 5D) were removed in 2013 from the Radiological Groundwater Protection Program (RGPP) prematurely prior to meeting the requirement of two consecutive samples measure <LLD (200 pCi/L) for tritium.

After identifying this issue the previously abandoned wells were re-drilled so that samples could be obtained.

The wells at these locations will remain until two consecutive <LLD measurements are obtained to support the closure of the consent order.

The following wells were missed during routine monitoring in 2015; MW-103 and 0WM31P. The Station RGPP requires the wells designated as detection wells to be sampled and analyzed for tritium on a quarterly basis. The aforementioned locations were not sampled during one or more of the quarters in 201

5. Reasons for lack of sampling include well condition deficiencies (0WM31P) and inaccessibility due to damage and downed trees surrounding the well as a result of tornado activity (MW

-103).

The Station RGPP also requires designated detection wells be analyzed for gamma

-radionuclides, gross

-alpha and beta, and strontium 89/90 on an annual basis. The well at MW

-103 had these analyses performed during the third quarter of 2015 and not the second quarter of 2015 as scheduled due to well inaccessibility from the tornado activity mentioned above.

B. Groundwater Results Groundwater

Samples were collected from on and off

-site wells throughout the year in accordance with the Station radiological groundwater protection program. Analytical results and anomalies are discussed below.

Tritium Samples from all locations were analyzed for tritium activity. Tritium values ranged from the lower detection limit to 3 , 2 0 0 pCi/l The wells with tritium results greater than the alert level of 2000 pCi/L were identified at locations MW

-4, MW-6 and MW-BW-144D along the west side of the Turbine Building. These wells are located onsite and are not available as a drinking water source

. Some contamination still exists and monitoring is ongoing (Table B-I.1, Appendix B)

. Strontium Strontium-89 and Strontium

-90 were analyzed for in 63 sample s. Strontiu m-89 was less than the required detection limit of 10.0 pCi/liter. Strontium

-90 was less than the required detection limit of 1.0 pCi/liter (Table B-I.1, Appendix B).

Gross Alpha and Beta (dissolved and suspended)

Gross Alpha and Gross Beta analyses in the dissolved and suspended fractions were performed on groundwater and surface water samples throughout the sampling year in 2015. Gross Alpha (dissolved) was not detected in any groundwater and surface water samples. Gross Alpha (suspended) was detected in two groundwater samples. The concentrations ranged from 1.3 to 3.0 pCi/L. Gross Beta (dissolved) was detected in 49 groundwater and surface water samples. The concentrations ranged from 1.7 to 47.1 pCi/L. Gross Beta (suspended) was detected in one groundwater sample. The concentration was 3.6 pCi/L.

(Table B-I.1, Appendix B)

. Hard-To-Detect Hard-To-Detect analyses were performed on one groundwater sample in 2015 as a result of a positive gross alpha result. The analyses included Am

-241, Cm-242, Cm-243/244, Pu

-238, Pu-239/240, U

-234, U-235 and U-238. Naturally occurring isotopes Uranium-234 and Uranium

-238 was detected in the sample at concentrations of 0.4 pCi/L and 0.5 pCi/L, respectively. All other hard-to-detect nuclides were not detected at concentrations greater than their respective MDCs. (Table B-I.3, Appendix B)

. Gamma Emitters

Naturally occurring K-40 was detected in five samples. The concentrations ranged from 51 to 1 5 4 pCi/L. No other gamma emitting nuclides were detected in any of the samples analyzed. (Table B-I.2, Appendix B)

C. Surface Water Results

Surface Water

Samples were collected from t wo surface water locations throughout the year in accordance with the station radiological groundwater protection program. Analytical results and anomalies are discussed below.

Tritium Samples from all locations were analyzed for tritium activity (Table

B-II.1, Appendix B). Tritium values ranged from the minimum detection limit to 2 89 pCi/l. Strontium Strontium-89 and Strontium

-90 were analyzed for in one sample. Strontium-89 was less than the required detection limit of 10.0 pCi/liter. Strontium

-90 was less than the required detection limit of 1.0 pCi/liter (Table B

-II.1, Appendix B).

Gamma Emitters No gamma emitting nuclides were detected in any of the samples analyzed (Table B-I I.2, Appendix B)

. D. Drinking Water Well Survey

Requested drinking water wells near Braidwood Station were sampled during the first and second quarter in 201 5. E. Summary of Results

- Inter-Laboratory Comparison Program

Inter-Laboratory Comparison Program results for TBE are presented in the AREO R. F. Leaks, Spills, and Releases

There are no new previously unidentified leaks or plumes at Braidwood Station.

G. Trends and Analyses Monitoring of remediation activities indicate that tritium concentrations in affected areas have remained relatively unchanged since 2010.

H. Investigations

No investigations took place in 201 5 as a result of groundwater sample result s. I. Actions Taken

1. Compensatory Actions

No compensatory actions were initiated in 201

5. 2. Installation of Monitoring Wells No new monitoring wells were installed in 201

5. 3. Actions to Recover/Reverse Plumes No actions were undertaken to recover/reverse plumes in 20 1 5. 4. Well Reduction Efforts

Sampling and monitoring of various well locations was ceased during the third quarter 2015. These wells were used during and after remediation activities completed under the March 11, 2010 Consent Order. On March 28, 2013 the Illinois EPA confirmed that remediation was complete at the sites subject to the March 11, 2010 Consent Order within letters sent to Exelon. In these same letters the Illinois EPA approved termination of pumping in recovery wells, cessation of sampling of most of the monitoring wells and the abandonment of wells not being used at these remediation sites

APPENDIX A LOCATION DESIGNATION

Intentionally left blank TABLE A-1: Radiological Groundwater Protection Program - Sampling Locations, Braidwood Station, 2015 ______________________________________________________________________________________

Station Code Sample Description BL-03 Monitoring Well BL-06 Monitoring Well BL-06D Monitoring Well BL-09D Monitoring Well BL-10D Monitoring Well BL-11 Monitoring Well BL-11D Monitoring Well BL-12D Monitoring Well BL-13D Monitoring Well BL-14D Monitoring Well BL-15D Monitoring Well BL-16D Monitoring Well BL-17D Monitoring Well BL-18D Monitoring Well BL-21 Monitoring Well BL-22 Monitoring Well BL-23 Monitoring Well BL-24 Monitoring Well BL-25 Monitoring Well BL-26 Monitoring Well BL-27 Monitoring Well D-2D Surface Water D-3D Surface water DITCH (DS-2) Surface Water EXELON POND Surface Water F-1D Monitoring Well F-3D Monitoring Well F-3DR Monitoring Well F-4D Monitoring Well F-5D Monitoring Well F-6D Monitoring Well F-8 D Monitoring Well F-9D Monitoring Well MW-102R Monitoring Well MW-103 Monitoring Well MW-105 Monitoring Well MW-105D Monitoring Well MW-106D Monitoring Well MW-107 Monitoring Well MW-109D Monitoring Well MW-11 Monitoring Well MW-110 Monitoring We ll MW-11 1 Monitoring Well MW-111DR Monitoring Well MW-112D Monitoring Well MW-113 Monitoring Well MW-113DR Monitoring Well MW-13 Monitoring Well MW-130D Monitoring Well MW-131D Monitoring Well MW-132D Monitoring Well

TABLE A-1: Radiological Groundwater Protection Program - Sampling Locations, Braidwood Station, 2015 ______________________________________________________________________________________

Station Code Sample Description MW-133D Monitoring Well MW-1 34D Monitoring Well MW-135D Monitoring Well MW-136D Monitoring Well MW-137D Monitoring Well MW-138D Monitoring Well MW-139D Monitoring Well MW-14 Monitoring Well MW-140D Monitoring Well MW-141D Monitoring Well MW-142D Monitoring Well MW-143D Monitoring Well MW-144D Monitoring Well MW-145D Monitoring Well MW-154 Monitoring Well MW-155 Monitoring Well MW-156 Monitoring Well MW-158D Monitoring Well MW-159D Monitoring Well MW-160D Monitoring Well MW-161D Monitoring Well MW-162D Monitoring We ll MW-2 Monitoring Well MW-22 Monitoring Well MW-4 Monitoring Well MW-5 Monitoring Well MW-6 Monitoring Well MW-7 Monitoring Well MW-9 Monitoring Well MW-BW-201BD Monitoring Well MW-BW-201I Monitoring Well MW-BW-201S Monitoring Well MW-BW-202I Monitoring Well MW-BW-202S Monitoring Well MW-BW-203I Monitoring Well MW-BW-203S Monitoring Well MW-BW-204I Monitoring Well MW-BW-205I Monitoring Well MW-BW-206I Monitoring Well MW-BW-207I Monitoring Well MW-BW-208BD Monitoring Well OWM31P Monitoring Well P-2D Monitoring Well P-4D Monitoring Well P-5D Monitoring Well P-13D Monitoring Well P-14D Monitoring Well RW-10 Monitoring Well RW-5 Monitoring Well

TABLE A-1: Radiological Groundwater Protection Program - Sampling Locations, Braidwood Station, 2015 ______________________________________________________________________________________

Station Code Sample Description RW-6 Monitoring Well RW-7 Monitoring Well RW-8 Monitoring Well RW-9 Monitoring Well S-1D Monitoring Well S-2D Monitoring Well S-4 Monitoring Well S-4D Monitoring Well S-5 Monitoring Well S-6 Monitoring Well S-7D Monitoring Well S-8 Monitoring Well S-8DR Monitoring Well SG-BW-105 Surface Water SG-BW-106 Surface Water SW-101 Surface Water SW-102 POINT C Surface Water SW-103 Surface Water SW-104 A DITCH Surface Water TB-20 Monitoring Well TB-20D Monitoring Well TB-21 Monitoring Well TB-21D Monitoring Well TB-22 Monitoring Well TB-22D Monitoring Well TB-23 Monitoring Well T B-23D Monitoring Well TB-24 Monitoring Well TB-24D Monitoring Well TB-25 Monitoring Well TB-25D Monitoring Well TB-2 6 D Monitoring Well VB10-1 Monitoring Well VB10-1R Monitoring Well VB1-1 Monitoring Well VB1-10 Monitoring Well VB1-10D Monitoring Well VB11-1 Monitoring Well VB1-11 Monitoring Well VB1-11D Monitoring Well VB1-12D Monitoring Well VB1-2 Monitoring Well VB1-2D Monitoring Well VB1-3 Monitoring Well VB1-3D Monitoring Well VB1-4 Monitoring Well VB1-4D Monitoring Well VB1-5 Monitoring Well VB1-5D Monitoring Well

TABLE A-1: Radiological Groundwater Protection Program - Sampling Locations, Braidwood Station, 2015 ______________________________________________________________________________________

Station Code Sample Description VB1-6 Monitoring Well VB1-6D Monitoring Well VB 1-7 Monitoring Well VB 1-7D Monitoring Well VB1-8 Monitoring Well VB1-8D Monitoring Well VB1-9 Monitoring Well VB1-9D Monitoring Well VB2-10 Monitoring Well VB2-10D Monitoring Well VB2-11 Monitoring Well VB2-11D Monitoring Well VB2-12 Monitoring Well VB2-12D Monitoring Well VB2-13 Monitoring Well VB2-13D Monitoring Well VB2-14 Monitoring Well VB2-14D Monitoring Well VB2-15D Monitoring Well VB2-16 Monitoring Well VB2-16D Monitoring Well VB2-17 Monitoring Well VB2-17D Monitoring Well VB2-2D Monitoring Well VB2-5D Monitoring Well VB2-6D Monitoring Well VB2-7D Monitoring Well VB2-9D Monitoring Well VB3-10D Monitoring Well VB3-2 Monitoring Well VB3-4D Monitoring Well VB3-7D Monitoring Well VB3-9D Monitoring Well VB4-1 Monitoring Well VB4-5D Monitoring Well VB4-6D Monitoring Well VB5-2 Monitoring Well VB6-1 Monitoring Well VB7-1 Monitoring Well VB8-2R Monitoring Well VB9-1 Monitoring Well

Figure A-1 Sampling Locations near the Site Boundary of Braidwood Station, 2015 Figure A-2 Sampling Locations near the Site Boundary of Braidwood Station, 2015 Figure A-3 Distant Sampling Locations of the Braidwood Station, 2015

Intentionally left blank APPENDIX B

DATA TABLES

Intentionally left blank TABLE B-I.1CONCENTRATIONS OF TRITIUM, STRONTIUM, GROSS ALPHA, ANDGROSS BETA IN GROUNDWATER SAMPLES COLLECTED IN THEVICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMACOLLECTIONSITEDATEH-3Sr-89Sr-90Gr-A (Dis)Gr-A (Sus)Gr-B (Dis)Gr-B (Sus)BL-0301/17/15<183BL-0304/11/15<164BL-1101/17/15<182BL-1104/11/15<162DS-203/11/15<179DS-206/24/15<181<6.6<0.5<1.0<1.23.6+/-1.0<2.2DS-208/28/15<196DS-210/07/15<184F-1D03/19/15<182F-1D06/18/15<172F-3DR03/19/15<178F-3DR06/18/15<175F-4D03/19/15<179F-4D06/17/15<175F-5D03/19/15<178F-5D06/17/15<174F-6D03/19/15<180F-6D06/18/15<175F-8D03/19/15<193F-8D06/18/15<175F-9D03/19/15<167F-9D06/18/15<173MW-102R01/17/15<180MW-102R04/11/15<163MW-102R08/28/15<197MW-102R10/07/15<185MW-10303/11/15<174MW-10309/09/15Original<196<6.7<0.8<1.13.0+/-1.6<1.63.6+/-1.8MW-10309/09/15Reanalysis 1

<1.12.6+/-1.1MW-10309/09/15Reanalysis 2

<1.14.0+/-1.3MW-109D03/11/15<175MW-109D04/12/15<167<5.2<0.7<1.3<0.61.7+/-0.9<1.4MW-1101/17/15 238+/-127MW-1104/05/15 310+/-130<4.7<0.5<1.8<0.43.3+/-1.0<1.3MW-1108/25/15 196+/-128MW-1110/18/15<200MW-111DR03/11/15<172MW-111DR05/06/15<195<5.2<0.9<1.01.3+/-0.7<1.3<1.6MW-112D03/09/15<174MW-112D05/06/15<184<4.7<0.7<1.5<0.43.0+/-1.2<1.5MW-11303/09/15<177MW-11306/24/15<182<6.8<0.8<2.1<0.62.5+/-1.4<1.4MW-130D03/11/15<172MW-130D04/12/15<161<5.1<0.7<1.3<0.62.0+/-0.9<1.4MW-131D03/11/15<176MW-131D04/12/15<176<5.3<0.6<1.5<0.73.9+/-1.1<1.5MW-134D03/09/15<175MW-134D05/06/15<184<5.5<0.7<0.6<0.41.8+/-1.1<1.5MW-135D03/18/15<177<3.7<0.6<1.2<0.4<3.0<1.7MW-135D06/17/15<173<5.6<0.7<1.4<0.52.2+/-1.0<1.7MW-136D03/18/15<174<4.5<0.7<2.7<0.43.9+/-2.4<1.7 TABLE B-I.1CONCENTRATIONS OF TRITIUM, STRONTIUM, GROSS ALPHA, ANDGROSS BETA IN GROUNDWATER SAMPLES COLLECTED IN THEVICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMACOLLECTIONSITEDATEH-3Sr-89Sr-90Gr-A (Dis)Gr-A (Sus)Gr-B (Dis)Gr-B (Sus)MW-136D06/18/15<175<6.4<0.6<2.2<1.23.3+/-1.6<2.5MW-137D03/18/15<176<3.3<0.6<1.0<0.42.7+/-1.0<1.7MW-137D06/17/15<175<5.4<0.5<1.3<0.53.1+/-0.9<1.7MW-138D03/18/15<173<3.5<0.5<2.1<0.43.0+/-1.2<1.7MW-138D06/17/15<169<5.5<0.5<1.8<0.53.0+/-1.2<1.7MW-139D03/18/15<174<6.5<0.8<1.2<0.419.8+/-1.4<1.7MW-139D06/18/15<176<4.5<0.7<1.0<0.522.6+/-1.5<1.7MW-141D02/07/15 707+/-150MW-141D03/18/15 692+/-147MW-141D04/19/15 631+/-148<7.7<0.7<4.2<0.647.1+/-2.8<1.5MW-141D08/25/15 342+/-139MW-141D10/11/15 444+/-136MW-142D02/07/15 1450+/-207MW-142D04/19/15 938+/-160<5.3<0.5<5.5<0.625.7+/-2.8<1.5MW-142D08/24/15 1180+/-184MW-142D10/18/15Original 1500+/-215MW-142D10/18/15Reanalysis 1700+/-232MW-143D03/18/15 232+/-122MW-143D04/05/15<169<5.9<0.6<3.7<0.46.8+/-1.5<1.3MW-143D08/27/15 288+/-137MW-143D10/17/15<190MW-144D01/17/15 1290+/-185MW-144D04/22/15Original 1130+/-175<6.3<0.8<5.3<0.612.3+/-1.8<1.5MW-144D04/22/15Recount12.1+/-2.5MW-144D08/26/15Original 2010+/-266MW-144D08/26/15Reanalysis 2290+/-286MW-144D10/11/15Original 2020+/-262MW-144D10/11/15Reanalysis 2040+/-262MW-145D03/19/15<172<3.2<0.5<0.8<0.4<1.2<1.7MW-145D06/18/15<176<5.3<0.6<0.9<0.5<1.4<1.7MW-145D09/23/15<185MW-145D12/09/15<189MW-15403/12/15 289+/-128<8.7<0.7<0.8<0.62.9+/-0.7<1.5MW-15405/07/15 334+/-133<5.5<0.9<0.6<0.62.1+/-0.7<1.5MW-15408/26/15<195<3.1<0.6<0.6<0.82.6+/-0.7<1.6MW-15410/25/15<192<7.4<0.7<0.8<0.62.3+/-0.7<1.6MW-15503/12/15 260+/-126<8.3<0.7<1.0<0.61.7+/-0.7<1.5MW-15505/07/15 227+/-128<6.0<0.8<0.9<0.72.6+/-0.8<1.7MW-15508/27/15<195<6.5<0.7<1.1<0.83.0+/-1.2<1.6MW-15510/25/15<190<6.1<0.8<1.3<0.63.5+/-1.0<1.6MW-158D03/18/15<173<5.3<0.6<0.9<0.439.4+/-3.7<1.7MW-158D06/18/15<174<5.2<0.6<1.0<0.543.1+/-1.9<1.7MW-159D01/17/15 390+/-137<3.5<1.0<1.9<1.26.7+/-1.3<2.3MW-159D04/12/15 186+/-112<5.4<0.7<3.9<0.66.5+/-1.4<1.4MW-159D08/24/15 266+/-136<3.5<0.8<1.6<0.86.1+/-1.4<1.6MW-159D10/18/15<199<6.5<0.9<1.6<0.74.0+/-1.1<2.2MW-162D01/17/15 784+/-159MW-162D04/05/15 761+/-149<6.2<0.6<1.9<0.45.5+/-1.1<1.3MW-162D08/24/15 591+/-151MW-162D10/18/15 610+/-153MW-203/18/15Original 800+/-153 TABLE B-I.1CONCENTRATIONS OF TRITIUM, STRONTIUM, GROSS ALPHA, ANDGROSS BETA IN GROUNDWATER SAMPLES COLLECTED IN THEVICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMACOLLECTIONSITEDATEH-3Sr-89Sr-90Gr-A (Dis)Gr-A (Sus)Gr-B (Dis)Gr-B (Sus)MW-203/18/15Recount 878+/-160MW-203/18/15Reanalysis 1060+/-167MW-205/07/15 682+/-152<4.6<0.8<1.3<0.64.5+/-2.1<1.5MW-209/09/15 370+/-141MW-210/11/15 375+/-132MW-401/17/15 1460+/-198MW-404/18/15Original 3200+/-373<8.0<0.7<8.0<0.4<5.3<1.4MW-404/18/15Recount 3240+/-370MW-408/25/15 1290+/-199MW-410/22/15 1300+/-197MW-501/17/15 383+/-135MW-503/18/15Original 734+/-149MW-503/18/15Recount 880+/-159MW-503/18/15Reanalysis 829+/-156MW-504/05/15 702+/-150<7.0<0.8<1.4<0.4<1.1<1.3MW-508/26/15 302+/-136MW-510/11/15 435+/-136MW-602/07/15 2190+/-276MW-604/18/15Original 1020+/-166<7.2<1.0<7.7<0.311.6+/-6.1<1.4MW-604/18/15Recount 1060+/-165MW-608/25/15 895+/-163MW-610/03/15 914+/-164MW-703/18/15Original 973+/-163MW-703/18/15Recount 1330+/-185MW-703/18/15Reanalysis 1220+/-176MW-704/18/15 743+/-159<9.3<0.8<1.4<0.32.1+/-1.2<1.4MW-708/25/15 788+/-158MW-710/22/15 1160+/-184MW-BW-201S01/17/15 393+/-137MW-BW-201S04/10/15 447+/-129<6.1<0.9<1.3<0.68.4+/-1.4<1.4MW-BW-201S09/18/15 425+/-141MW-BW-201S10/17/15 215+/-127MW-BW-202S03/13/15 464+/-137MW-BW-202S04/10/15 295+/-119<4.9<0.7<4.3<0.610.0+/-1.9<1.4MW-BW-202S08/24/15 271+/-137MW-BW-202S10/17/15 396+/-136MW-BW-203S03/13/15 202+/-117MW-BW-203S04/10/15 196+/-112<4.5<1.0<1.1<0.67.6+/-1.2<1.4MW-BW-203S08/24/15<194MW-BW-203S10/17/15 236+/-128MW-BW-207I02/07/15 1040+/-173MW-BW-207I05/07/15 1050+/-171<4.6<0.6<7.3<0.615.7+/-5.3<1.5MW-BW-207I08/25/15 995+/-172MW-BW-207I10/11/15 1090+/-176MW-P2D06/17/15<172OWM31P12/31/15<193P-13DR08/20/15Original 261+/-134P-13DR08/20/15Recount 412+/-117P-13DR08/20/15Reanalysis 256+/-123P-13DR12/09/15<190P-2D03/18/15<175 TABLE B-I.1CONCENTRATIONS OF TRITIUM, STRONTIUM, GROSS ALPHA, ANDGROSS BETA IN GROUNDWATER SAMPLES COLLECTED IN THEVICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMACOLLECTIONSITEDATEH-3Sr-89Sr-90Gr-A (Dis)Gr-A (Sus)Gr-B (Dis)Gr-B (Sus)P-4DR08/20/15<192P-4DR09/23/15<190P-4DR12/09/15<184PW-00601/20/15<172PW-00604/08/15<174PW-006P01/20/15<173PW-006P04/08/15<174PW-01101/20/15<171PW-01104/08/15<178PW-01601/20/15<169PW-01604/08/15<173PW-1301/20/15<169PW-1304/08/15<174RW-1003/25/15<175RW-1005/06/15<181<5.0<0.7<1.0<0.42.7+/-0.9<1.5RW-503/12/15Original 198+/-123RW-503/12/15Recount 263+/-126RW-506/24/15<182<6.1<0.6<2.7<0.63.0+/-1.8<1.4RW-603/11/15 1420+/-194RW-604/12/15 1110+/-161<5.7<0.8<1.9<0.65.5+/-1.3<1.4RW-608/28/15 578+/-149RW-608/28/15 420+/-142RW-610/07/15 513+/-143RW-703/11/15Original 469+/-135RW-703/11/15Recount 450+/-138RW-704/12/15 424+/-128<5.1<0.6<1.5<0.74.2+/-1.0<2.0RW-901/17/15<182RW-904/11/15<161<5.2<0.7<1.1<0.43.7+/-1.0<1.5SG-BW-10208/28/15<197SG-BW-10210/07/15 188+/-125VB-106/24/15<187VB-1-9DR08/20/15Original 275+/-138VB-1-9DR08/20/15Recount 418+/-120VB-1-9DR08/20/15Reanalysis 277+/-124VB-1-9DR09/22/15<193VB-1-9DR12/09/15<188VB-10-1R03/17/15<179VB-10-1R06/16/15<185VB-10-1R09/22/15<192VB-10-1R12/08/15<186VB-11-103/18/15<176VB-11-106/17/15<172VB-11-109/23/15<188VB-11-112/09/15<185VB-2-5DR08/20/15<192VB-2-5DR09/23/15<190VB-2-5DR12/09/15Original 191+/-124VB-2-5DR12/09/15Recount 245+/-132VB-2-5DR12/09/15Reanalysis 250+/-131VB-3-4DR08/20/15<194VB-3-4DR09/23/15<188 TABLE B-I.1CONCENTRATIONS OF TRITIUM, STRONTIUM, GROSS ALPHA, ANDGROSS BETA IN GROUNDWATER SAMPLES COLLECTED IN THEVICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMACOLLECTIONSITEDATEH-3Sr-89Sr-90Gr-A (Dis)Gr-A (Sus)Gr-B (Dis)Gr-B (Sus)VB-3-4DR12/09/15<183VB-4-103/17/15<178VB-4-106/16/15<169VB-5-203/18/15<174VB-5-206/16/15<186VB-5-209/23/15<189VB-5-212/09/15<185VB-6-103/17/15<177VB-6-106/16/15<175VB-6-109/22/15<190VB-6-112/08/15<188VB-7-103/17/15<178VB-7-106/16/15<167VB-7-109/22/15<187VB-7-112/08/15<187VB-8-2R03/17/15<179VB-8-2R06/16/15<172VB-8-2R09/22/15<188VB-8-2R12/08/15<189VB-9-103/17/15<174VB-9-106/16/15<183VB-9-109/22/15<188VB-9-112/08/15<189VB-P-13DR09/22/15<188VB1-108/27/15<198VB1-110/25/15<192VB3-201/17/15<180VB3-204/11/15<163VB3-208/28/15<195VB3-210/07/15<187VBI-103/25/15<185 BOLDED VALUES INDICATE LLD COULD NOT BE MET DUE TO AGE OF SAMPLE AT TIME OF RECEIPT AT LABORATORYTABLE B-I.2CONCENTRATIONS OF GAMMA EMITTERS IN GROUNDWATER SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMASITECOLLECTIONBe-7K-40Mn-54Co-58Fe-59Co-60Zn-65Nb-95Zr-95I-131Cs-134Cs-137Ba-140La-140DATEDS-206/24/15<20<18<2<2<5<2<4<2<4<14<2<2<24<10MW-10309/09/15<20<54<2<2<5<2<4<2<4<13<2<2<21<7MW-109D04/12/15<14<13<1<2<3<1<3<2<3<9<1<1<15<4MW-1104/05/15<18<17<2<2<4<2<3<3<4<13<2<2<22<8MW-111DR05/06/15<14<10<1<1<3<1<3<2<2<13<1<1<19<5MW-112D05/06/15<14<31<1<1<3<1<2<1<2<15<1<1<19<7MW-11306/24/15<14<21<1<1<3<1<2<2<3<11<1<1<16<5MW-130D04/12/15<11<11<1<1<3<1<2<1<2<7<1<1<12<4MW-131D04/12/15<15<15<1<2<4<1<3<2<3<8<1<2<15<5MW-134D05/06/15<14<11<1<2<3<1<3<2<3<14<1<1<19<7MW-135D03/18/15<8<6<1<1<2<1<1<1<2<7<1<1<10<3MW-135D06/17/15<55 100+/-58<5<5<10<7<10<7<12<12<5<6<25<7MW-136D03/18/15<14<24<1<1<4<1<3<2<3<12<1<1<18<5MW-136D06/18/15<63<114<6<6<11<7<12<7<11<12<6<8<35<11MW-137D03/18/15<10<24<1<1<2<1<2<1<2<9<1<1<13<3MW-137D06/17/15<49<117<8<6<15<6<15<7<11<12<6<6<38<11MW-138D03/18/15<11<24<1<1<3<1<2<1<2<10<1<1<14<5MW-138D06/17/15<51<107<5<5<12<6<9<5<10<12<5<4<29<8MW-139D03/18/15<9<23<1<1<2<1<2<1<2<9<1<1<12<4MW-139D06/18/15<61<58<6<8<13<7<14<9<12<12<6<9<35<12MW-141D04/19/15<20 51+/-27<2<2<5<2<4<2<4<14<2<2<22<7MW-142D04/19/15<18<14<2<2<4<1<3<2<3<13<2<2<20<5MW-143D04/05/15<16<13<1<1<3<1<3<1<3<12<1<1<19<5MW-144D04/22/15<25<21<2<2<5<2<5<3<5<13<2<2<25<8MW-145D03/19/15<11<25<1<1<3<1<2<1<2<9<1<1<12<4MW-145D06/18/15<44<56<5<5<11<6<10<5<9<8<4<5<24<7MW-15403/12/15<9<7<1<1<3<1<2<1<2<16<1<1<18<6MW-15405/07/15<15<10<1<1<4<1<2<1<3<15<1<1<21<5MW-15408/26/15<16<34<2<2<4<2<3<2<3<14<1<2<21<7MW-15410/25/15<13<14<1<1<3<1<3<2<3<6<1<1<11<4MW-15503/12/15<6<5<1<1<1<0<1<1<1<10<1<1<12<3MW-15505/07/15<16<42<2<2<4<1<3<2<3<14<1<1<22<6 BOLDED VALUES INDICATE LLD COULD NOT BE MET DUE TO AGE OF SAMPLE AT TIME OF RECEIPT AT LABORATORYTABLE B-I.2CONCENTRATIONS OF GAMMA EMITTERS IN GROUNDWATER SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMASITECOLLECTIONBe-7K-40Mn-54Co-58Fe-59Co-60Zn-65Nb-95Zr-95I-131Cs-134Cs-137Ba-140La-140DATEMW-15508/27/15<18<13<2<2<4<2<3<2<3<14<2<2<22<5MW-15510/25/15<13<11<1<1<3<1<3<1<2<6<1<1<11<4MW-158D03/18/15<12<11<1<1<3<1<2<1<2<10<1<1<16<5MW-158D06/18/15<59 128+/-63<7<7<14<7<13<7<12<13<7<7<30<11MW-159D01/17/15<22<21<2<2<5<2<5<3<4<9<2<2<18<6MW-159D04/12/15<17<13<1<2<4<1<3<2<3<13<1<2<19<5MW-159D08/24/15<14<21<1<1<3<1<2<2<3<14<1<1<19<5MW-159D10/18/15<59<122<6<8<13<4<11<8<10<15<5<7<38<11MW-162D04/05/15<17<49<1<2<4<2<3<2<3<12<1<2<20<5MW-205/07/15<14<26<1<1<3<1<2<2<2<14<1<1<21<6MW-404/18/15<17<42<2<2<4<2<3<2<3<13<1<2<19<6MW-504/05/15<19<32<2<2<4<2<4<2<4<14<2<2<21<6MW-604/18/15<20<17<2<2<5<2<4<2<4<13<2<2<21<7MW-704/18/15<16<29<1<2<4<2<3<2<3<12<1<1<18<6MW-BW-201S04/10/15<9<8<1<1<2<1<1<1<2<7<1<1<11<3MW-BW-202S04/10/15<13<8<1<1<3<1<2<1<2<11<1<1<15<3MW-BW-203S04/10/15<14 154+/-27<1<2<4<1<3<2<3<12<1<1<17<7MW-BW-207I05/07/15<14<11<1<1<4<1<3<2<3<15<1<1<18<7MW-P2D06/17/15<49<75<7<6<11<5<10<7<10<11<5<6<28<8P-2D03/18/15<13<8<1<1<3<1<2<1<2<12<1<1<18<4RW-1005/06/15<10 62+/-32<1<1<3<1<2<2<2<13<1<1<17<5RW-506/24/15<17<30<1<2<4<1<3<2<3<14<1<2<20<6RW-604/12/15<15<16<1<2<4<1<3<2<3<11<1<1<17<6RW-704/12/15<16<14<1<2<3<2<3<2<3<11<1<1<17<5RW-904/11/15<14<42<1<2<3<1<2<2<3<11<1<1<16<5 TABLE B-I.3CONCENTRATIONS OF HARD TO DETECTS IN GROUNDWATER SAMPLESCOLLECTED AS PART OF THE RADIOLOGICAL GROUNDWATERPROTECTION PROGRAM, BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMASITECOLLECTIONAm-241 Cm-242 Cm-243/244 Pu-238 Pu-239/240 U-235 Fe-55Ni-63DATEMW-10309/09/15<0.1<0.1<0.2<0.2<0.10.4+/-0.3<0.10.5+/-0.3U-238 U-234 TABLE B-II.1CONCENTRATIONS OF TRITIUM, STRONTIUM, GROSS ALPHA, ANDGROSS BETA IN SURFACE WATER SAMPLES COLLECTED IN THEVICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMACOLLECTIONSITEDATEH-3Sr-89Sr-90Gr-A (Dis)Gr-A (Sus)Gr-B (Dis)Gr-B (Sus)SW-0501/20/15<173SW-0504/08/15Original<170SW-0504/08/15Recount<186SW-10203/11/15 289+/-128SW-10204/11/15 175+/-112<4.4<0.7<1.3<0.84.6+/-1.0<1.9 TABLE B-II.2CONCENTRATIONS OF GAMMA EMITTERS IN SURFACE WATER SAMPLESCOLLECTED IN THE VICINITY OF BRAIDWOOD STATION, 2015RESULTS IN UNITS OF PCI/LITER +/- 2 SIGMASITECOLLECTIONBe-7K-40Mn-54Co-58Fe-59Co-60Zn-65Nb-95Zr-95I-131Cs-134Cs-137Ba-140La-140DATESW-10204/11/15<14<24<1<1<3<1<2<2<3<11<1<1<16<5 May 11, 2016 BW160031 U.S. Nuclear Regulatory Commission Attn: Document Control Desk Washington, D.C. 20555-0001